Loading...
The URL can be used to link to this page
Your browser does not support the video tag.
Home
My WebLink
About
Attachment 3a-07 - Phase I ESA (Part 1) Redacted
Phase I Environmental Site Assessment Assessor’s Parcel Number 644-040-01 517 Shinohara Lane, Chula Vista, CA 91911 VWP-OP Shinohara Owner, LLC 2390 East Camelback Road, Suite 305 Phoenix, Arizona 85016 8799 Balboa Avenue, Suite 290 San Diego, CA 92123 858-571-5500 01221156.01 | July 13, 2021 APPENDIX I - PART 1 Phase I Environmental Site Assessment www.scsengineers.com i July 13, 2021 Project Number: 01221156.01 Mr. Steven Schwarz VWP-OP Shinohara Owner, LLC 2390 East Camelback Road, Suite 305 Phoenix, Arizona 85016 Subject: Phase I Environmental Site Assessment (Assessment) Site: Assessor’s Parcel Number (APN) 644-040-01 517 Shinohara Lane, Chula Vista, California 91911 Dear Mr. Schwarz: SCS Engineers (SCS) is pleased to present this report (Report) of the Assessment of the above-described Site. This Report summarizes the results of the Assessment that was conducted in order to evaluate the Site’s current environmental conditions. The work described in this Report was performed by SCS in general accordance with Exhibit 01 to the Master Services Agreement Contract) between SCS and VWP-OP Shinohara Owner, LLC (Client). Exhibit 01 was fully executed on June 22, 2021. The Contract was fully executed on June 21, 2021. Because your full understanding of the Assessment is important to us, SCS recommends that you read the Report in its entirety. However, if time does not allow you a complete reading, summaries may be found in text boxes at the end of each section (pages 11, 21, and 26), and our conclusions and recommendations may be found on page 26. A glossary of terms commonly used in environmental assessments is also provided in the Appendices to this Report. SCS enjoyed working with you on this project. Providing economical environmental solutions to meet your needs is more than our goal—it is our mission and the measure of our success. If we may assist you in any way, now or in the future, please call our office at (858) 571-5500. Sincerely, Allison O’Neal Luke Montague, MESM, PG 8071 Staff Professional Vice President SCS ENGINEERS SCS ENGINEERS Phase I Environmental Site Assessment www.scsengineers.com ii Table of Contents Section Page 1 Background ................................................................................................................................... 4 2 Standards Background ................................................................................................................. 4 3 Objective ....................................................................................................................................... 6 4 Scope of Services .......................................................................................................................... 6 Site Reconnaissance ......................................................................................................................... 6 General Information ................................................................................................................. 6 Site Buildings ............................................................................................................................ 6 Site Grounds ............................................................................................................................. 7 Hazardous Materials/Petroleum Products ............................................................................. 7 Hazardous Wastes.................................................................................................................... 7 Indications of Releases of Hazardous Materials/Wastes or Petroleum Products ............... 7 On-Site Utilities ......................................................................................................................... 7 Site Research ..................................................................................................................................... 8 Department of Environmental Health (DEH) File Review ....................................................... 8 Review of Client-Provided Documents .................................................................................... 8 Fire Department Records Review ............................................................................................ 9 Building Department Records Review .................................................................................... 9 San Diego Air Pollution Control District (SDAPCD) Records Review ...................................... 9 San Diego Industrial Wastewater Program (IWP) Records Review ....................................... 9 Regional Water Quality Control Board (RWQCB) Records Review ......................................... 9 Interviews ........................................................................................................................................ 10 User Requirements ......................................................................................................................... 10 Data Gaps in Connection With Current Site Land Use ................................................................. 11 Topography, Geology, Hydrogeology, and Water Quality Survey .................................................. 11 Topography ............................................................................................................................ 11 Geology ................................................................................................................................... 11 Hydrogeology ......................................................................................................................... 12 Water Quality Survey ............................................................................................................. 12 Site Vicinity Reconnaissance and Off-Site Source Survey ............................................................ 13 Current Site Vicinity Conditions ............................................................................................ 13 Environmental Regulatory Database Report ....................................................................... 13 Additional SCS Research ...................................................................................................... 16 Brandywine Distribution Center/Tap Manufacturing LLC/Transpere, LLC/Keystone Automotive Industries/Jones, Lang, LaSalle Property Management/Lyon Technologies, 1670 & 1690 Brandywine Avenue, Adjacent to the East .................................................................. 16 H130637, Nypro San Diego, 505 Main Street, Adjacent to the South ................ 19 H208691, Fuller Ford Collision Center, 515 Main Street, Adjacent to the South ......................................................................................................... 20 California Division of Oil and Gas ............................................................................ 21 Data Gaps in Connection With Off-Site Sources ........................................................................... 21 Phase I Environmental Site Assessment www.scsengineers.com iii Historical Land Use Review ............................................................................................................ 22 Historical Site Land Use ........................................................................................................ 23 Historical Site Vicinity Land Use ........................................................................................... 24 Historical Adjacent Agricultural ............................................................................... 25 Data Gaps in Connection With the Historical Site Land Use ........................................................ 26 5 Conclusions and Recommendations ..........................................................................................26 6 Report Usage and Future Site Conditions ...................................................................................27 7 Likelihood Statements ................................................................................................................28 8 Special Contractual Conditions Between User and Environmental Professional .......................28 9 Endnotes .....................................................................................................................................28 Figures Figure 1 Four-Way Site Location Map Figure 2 Site and Site Vicinity Plan Figures 3a–3h Photographic Plates Appendices Glossary Department of Environmental Health Correspondence Client-Provided Documents City of Chula Vista Correspondence for Fire Department and Industrial Wastewater Records Building Department Record Correspondence Air Pollution Control District Correspondence Regional Water Quality Control Board Correspondence Environmental Regulatory Database Report Sanborn Fire Insurance Maps – No Coverage Letter City Directories Department of Environmental Health Correspondence for the Site Vicinity Résumés Phase I Environmental Site Assessment www.scsengineers.com 4 1 BACKGROUND Based on conversations with VWP-OP Shinohara Owner, LLC (Client) and a review of in-house databases, SCS Engineers (SCS) understands that 517 Shinohara Lane, Chula Vista, California 91911 (Site), consists of one approximately 9.56-acre parcel of land (Figure 1). The Site is currently a vacant and undeveloped lot. The Client is proposing to purchase the Site and develop it into an industrial building. A review of the in-house ParcelQuest database of information from the San Diego County Assessor’s Office provided the following information in connection with the Site. APN Address Area Description 644-040-01 517 Shinohara Lane 9.56 acres Vacant 2 STANDARDS BACKGROUND This Assessment was conducted in general accordance with the following: U.S. Environmental Protection Agency (EPA), 40 Code of Federal Regulations (CFR) 312, Standards and Practices for All Appropriate Inquiries; Final Rule (AAI) American Society for Testing and Materials (ASTM) Standard Practice for Phase I Environmental Site Assessment Process E1527-13 The scope, conditions, and limitations of Exhibit 01 The Client understands that the above-referenced EPA and ASTM standards were not developed to identify all environmental risk to property. The standards were developed to allow a user (Client) to qualify for the innocent purchaser defense, bona fide prospective purchaser defense, and contiguous property owner defense to the Comprehensive Environmental Response, Compensation, and Liability Act of 1980 (CERCLA, a.k.a. Superfund) liability. This Assessment is intended to constitute an appropriate inquiry into the previous ownership and uses of the property consistent with good commercial or customary practice, as part of the due diligence process required by CERCLA, the Superfund Amendments and Reauthorization Act of 1986, and the Small Business Liability Relief and Brownfields Revitalization Act of 2002 (collectively, Acts). While this Assessment may initially qualify the Client for a CERCLA defense, after purchase, there may be continuing obligations that must be implemented in order to preserve this defense through the term of property ownership. There may be additional requirements under state law that also apply. The Client should contact qualified legal counsel regarding matters of liability, interpretation of the Acts, and potential continuing obligations. Although it is outside the scope of this Assessment, SCS would be pleased to work with the Client’s legal counsel to develop and implement a strategy to preserve the Client’s CERCLA liability defenses through the term of its ownership. Phase I Environmental Site Assessment www.scsengineers.com 5 This Assessment focused on potential sources of hazardous substances and petroleum products that could be considered either a recognized environmental condition,1 controlled recognized environmental condition,2 or historical recognized environmental condition,3 and potentially a liability due to their presence in significant concentrations (e.g., above acceptable limits set by the federal, state, or local government) or due to the potential for exposure and risk due to contaminant migration and complete exposure pathways (e.g., soil vapor inhalation or groundwater ingestion). Materials that contain substances that are not currently deemed hazardous by the EPA or the California Environmental Protection Agency were not considered as part of this Assessment. Unless specifically included in SCS’ scope of services, building materials such as asbestos, lead- based paint, urea formaldehyde, and pressure-treated lumber, as well as lead in drinking water, are not considered in this Assessment, nor are building issues such as fire safety, indoor air quality (with the possible exception of vapor intrusion), mold, or similar matters. SCS did not evaluate the Site for compliance with land use, zoning, wetlands, or similar laws. This Assessment also excludes regulatory compliance, cultural and historic resources, industrial hygiene, health and safety, ecological resources, endangered species, and high-voltage power lines. This Assessment is not intended to be an environmental compliance audit. Hazardous substances occurring naturally in plants, soils, and rocks (e.g., heavy metals, naturally occurring asbestos, and radon) are not typically considered in these investigations. Similarly, construction debris (e.g., discarded concrete, asphalt) is not considered, unless obvious indications suggest that hazardous substances are likely to be present in significant concentrations or likely to migrate. An evaluation of business environmental risk associated with a parcel of commercial real estate may necessitate investigation beyond that included herein. 1 Recognized environmental conditions, as defined by ASTM, include the presence or likely presence of any hazardous substances or petroleum products in, on, or at a property: (1) due to any release to the environment; (2) under conditions indicative of a release to the environment; or (3) under conditions that pose a material threat of a future release to the environment. However, the term is not intended to include de minimis conditions (a condition that generally does not present a threat to human health or the environment and that generally would not be subject to an enforcement action if brought to the attention of appropriate governmental agencies). A condition considered de minimis is not a recognized environmental condition. 2 Controlled recognized environmental condition, as defined by ASTM, is a recognized environmental condition resulting from a past release of hazardous substances or petroleum products that has been addressed to the satisfaction of the applicable regulatory authority (for example, as evidenced by the issuance of a no further action letter or equivalent, or meeting risk-based criteria established by regulatory authority), with hazardous substances or petroleum products allowed to remain in place subject to the implementation of required controls (for example, property use restrictions, activity use limitations, institutional controls, or engineering controls). 3 Historical recognized environmental condition, as defined by ASTM, is a past release of any hazardous substances or petroleum products that has occurred in connection with the property and has been addressed to the satisfaction of the applicable regulatory authority or meeting unrestricted use criteria established by a regulatory authority, without subjecting the property to any required controls (for example, property use restrictions, activity and use limitations, institutional controls, or engineering controls). Phase I Environmental Site Assessment www.scsengineers.com 6 3 OBJECTIVE The objective of the scope of services was to assess the likelihood that recognized environmental conditions are present at the Site as a result of the current or historical Site land use or from a known and reported off-Site source. 4 SCOPE OF SERVICES The scope of services designed and conducted to meet the objective was as follows: Site Reconnaissance, Site Research, Interviews, and User Requirements Topography, Geology, Hydrogeology, and Water Quality Survey Site Vicinity Reconnaissance and Off-Site Source Survey Historical Site and Site Vicinity Land Use Review Identification of Data Gaps Data Evaluation, Figure Preparation, and Assessment Report Preparation SITE RECONNAISSANCE On July 1, 2021, SCS personnel conducted a Site reconnaissance to observe and document existing Site conditions.i The general Site location is shown in Figure 1, and a Site and Site Vicinity Plan is shown in Figure 2. Selected color photographs of the Site and Site vicinity are presented as Figures 3a through 3h. The Site grounds and Site perimeter were systematically traversed on foot during the Site reconnaissance. SCS personnel observed the Site features unaccompanied. General Information The following table summarizes general information in connection with the Site. APN 644-040-01 Address 517 Shinohara Lane, Chula Vista, California 91911 Area 9.56 acres Site Land Use Vacant, undeveloped land Occupant None Figure Reference Figures 3a-1 through 3f-2 Site Buildings No buildings were observed on Site. Phase I Environmental Site Assessment www.scsengineers.com 7 Site Grounds The Site grounds were observed to be vacant, undeveloped land (Figures 2 and 3a-1 through 3f-2). Concrete drainage channels were observed in the northeastern and east central portions of the Site Figures 3e-1 and 3f-2). After a review of the City of Chula Vista GIS Web Map including a map of their storm drain system,4 it does not appear that the drainage observed on Site is connected to the city’s storm drain system. Small piles of household trash and wood furniture, electronics, and debris were observed in various locations on Site (Figures 2 and 3e-2). Hazardous Materials/Petroleum Products No obvious indications of the storage or use of hazardous materials and/or petroleum products were observed at the Site during the Site reconnaissance. Hazardous Wastes No obvious indications of the generation of hazardous wastes were observed at the Site during the Site reconnaissance. Indications of Releases of Hazardous Materials/Wastes or Petroleum Products No obvious indications were observed that a release of hazardous materials/wastes or petroleum products had occurred at the Site. On-Site Utilities Gas and Electricity Reported to be San Diego Gas and Electric (SDG&E) High-power Transmission Lines None observed at or adjacent to the Site Storm Drains None observed to be located at the Site Source of Heating and Cooling None Potable Water Source None Wastewater Conveyance None No SDG&E transformers were observed to be located at the Site. No obvious indications of wells, cisterns, pits, sumps, dry wells, or bulk storage tanks were observed at the Site. 4 https://gisweb.chulavistaca.gov/cvmapper/ Phase I Environmental Site Assessment www.scsengineers.com 8 SITE RESEARCH Department of Environmental Health (DEH) File Review A review of the September 2010 DEH Hazardous Materials Management Division (HMMD) HE-17 database of facilities storing hazardous materials, generating hazardous wastes, and discharging unauthorized releases indicated that there is no regulatory file associated with the Site. In addition, the DEH was contactedii and indicated that there are no files associated with the Site. Review of Client-Provided Documents The Client provided a report titled Phase I Environmental Site Assessment Report, Industrial Land, 517 Shinohara Lane, Chula Vista, CA 91911, which was prepared by Partner Engineering and Science, Inc. (Partner) and dated January 16, 2018. This report provided the following findings, conclusions and recommendations in connection with the Site: A recognized environmental condition (REC) refers to the presence or likely presence of any hazardous substances or petroleum products in, on, or at a property: due to release to the environment; under conditions indicative of a release to the environment; or under conditions that pose a material threat of a future release to the environment. The following was identified during the course of this assessment: Based on subsurface investigations conducted at the east adjacent Brandywine Distribution Center sites, it appears that chlorinated hydrocarbons (TCE reported at concentrations of 1 l to 720 l) potentially originating from the up-gradient former Omar Rendering site and the Otay Landfill have impacted the groundwater at the east adjacent Brandywine Distribution Center sites, and the potential exists that chlorinated hydrocarbons originating from the former Omar Rendering site and the Otay Landfill have impacted the subsurface of the subject property. The Regional Water Quality Control Board (RWQCB), the lead oversight agency, reviewed a 1996 Soil and Groundwater Investigation report for the Brandywine Distribution Center case and in a letter dated November 15, 1996, summarized that volatile organic compounds (VOC) including trichloroethene (TCE), tetrachloroethene (PCE), and methylene chloride (MEC) had been discovered at elevated concentrations in groundwater beneath the sites, but not in the unsaturated soil zone. Even though the RWQCB cited that the former Omar Rendering site and the former Otay Landfill had not been clearly identified as the sources of impacted groundwater beneath the Brandywine Distribution Center, the RWQCB appeared to concur with the consultant's findings including the determination that the source of the impact was not related to historic or present activities at the Brandywine Distribution Center but from up-gradient sources. In the 1996 letter, the RWQCB stated that No Further Action (NFA) was required and that the RWQCB did not intend to pursue regulatory action against the current or former owners of the Brandywine Distribution Center. The case was granted regulatory closure on May 3, 2017. Based on the aforementioned, the potential exists that chlorinated hydrocarbons originating from the former Omar Rendering site and the Otay Landfill have impacted the subsurface of the subject property. The likely presence of subsurface contamination at the subject property is considered a recognized environmental condition. Phase I Environmental Site Assessment www.scsengineers.com 9 This assessment has revealed evidence of recognized environmental conditions and/or environmental issues in connection with the subject property. Based on the conclusions of this assessment, Partner recommends the following: The potential for vapor intrusion, from documented contaminants in up-gradient groundwater samples, should be evaluated through a limited subsurface investigation prior to development of the subject property.” SCS concurs with the above findings, which are discussed in further detail in the “Additional SCS Research” section below. Fire Department Records Review The City of Chula Vista Fire Department (CVFD) was contacted regarding hazardous materials/waste or UST records for the Site.iii The CVFD reported that they have no records for the Site. A copy of the SDFD letter is included in the Appendices. Building Department Records Review Chula Vista Building Department (CVBD) records were requested for the Site. The CVBD reported that there are no records maintained for the Site. A copy of the correspondence is included in the Appendices. San Diego Air Pollution Control District (SDAPCD) Records Review The SDAPCD was contacted iv regarding records for the Site. Mr. Radley Salamat reported that no records are maintained for the Site. A copy of the correspondence is included in the Appendices. San Diego Industrial Wastewater Program (IWP) Records Review The IWP was contactedv regarding records for the Site. The IWP reported that they have no records for the Site. A copy of the IWP letter is included in the Appendices. Regional Water Quality Control Board (RWQCB) Records Review The San Diego RWQCB was contacted vi regarding records for the Site. The following table summarizes the RWQCB records provided for the Site. Copies of the records are included in the Appendices. Year Description Reported Owner 1992 A Notice of Intent to comply with the terms of the general permit to discharge storm water associated with construction activity was issued Lawrence and Stephen Cushman 2007 Notice of Termination (NOT) to the general permit to discharge storm water associated with construction activity due to completion of the construction project Lawrence and Stephen Cushman Phase I Environmental Site Assessment www.scsengineers.com 10 Year Description Reported Owner 2007 The RWQCB approved the NOT for the Site Lawrence and Stephen Cushman Based on the absence of disposal violations and the approval of the NOT there is a low likelihood that a recognized environmental condition exists at the Site in connection with the review of the RWQCB records. INTERVIEWS The previously referenced EPA and ASTM standards require that attempts be made to conduct interviews with past and present owners and occupants of the Site to obtain information indicating recognized environmental conditions in connection with the Site. As part of this Assessment, the following contacts were either interviewed or attempts were made to conduct interviews. Contact Affiliation to Site Description Interview Date Ms. Sarina Davis Current Site owner representative Discussed below July 6, 2021 Ms. Davis, National Director of Real Estate of Encompass Health California Real Estate, LLC, Site owner’s representative who has been familiar with the Site for 2 years and 10 months, stated that, to her knowledge, hazardous materials and petroleum products were not used or stored at the Site and that hazardous wastes were not generated at the Site. Also, to her knowledge, there have been no releases of hazardous materials, petroleum products, and/or hazardous waste at the Site. Ms. Davis stated that she was not aware of environmental cleanup liens or activity and use limitations (e.g., engineering controls, deed restrictions) that have been recorded for the Site. She was not aware of pending or threatened litigation or administrative proceedings relevant to hazardous substances or petroleum products in, on, or from the Site. She was not aware of notices from governmental entities regarding possible violations of environmental laws or possible liability relating to hazardous substances or petroleum products at the Site. USER REQUIREMENTS In order to qualify for one of the landowner liability protections offered by the Small Business Liability Relief and Brownfields Revitalization Act of 2001 (discussed in the “Background” section), 40 CFR 312 requires that the user (Client) provide the following information to the environmental professional. Mr. Todd Dwyer completed the User Questionnaire on June 22, 2021. The following table summarizes the responses by the Client. Question Response Have environmental cleanup liens been filed or recorded against the Site? No Are activity or land use limitations in place at the Site, or have they been filed or recorded in the registry? No Phase I Environmental Site Assessment www.scsengineers.com 11 Does the user have specialized knowledge or experience in connection with the Site? No Does the purchase price being paid for the Site reasonably reflect the fair market value of the Site? Yes Is the Client aware of commonly known or reasonably ascertainable information about the Site that would indicate releases or threatened releases? No Are there obvious indications that point to the presence of contamination at the Site? No DATA GAPS IN CONNECTION WITH CURRENT SITE LAND USE Based on observations and research, and with the possible exception discussed below, there are no obvious indications of data gaps in connection with the current Site land use: The current Site owner did not have contact information for previous owners of the Site. Additionally, SCS was unable to find contact information for previous Site owners via online searches. Therefore, interviews were not conducted with previous Site owners. This data gap is not a significant data gap in our opinion based on the availability of other relevant information. Findings and Opinions—Current Site Land Use Based on observations and research, it is our opinion that there are no recognized environmental conditions at the Site as a result of the current Site land use. TOPOGRAPHY, GEOLOGY, HYDROGEOLOGY, AND WATER QUALITY SURVEY Topography A topographic map for the Site vicinity was reviewed and is summarized in the following table. Reported Elevation 150 to 240 feet above mean sea level Reported Slope Direction Slopes down to the south Source United States Geological Survey 7.5 Minute Topographic Map, Imperial Beach Quadrangle, California – San Diego County, 2018 Geology A geological map for the Site vicinity was reviewed and is summarized in the following table. Reported Formation Old alluvial flood-plain deposits (Qoa), undivided late to middle Pleistocene aged Phase I Environmental Site Assessment www.scsengineers.com 12 Reported Description Fluvial sediments deposited on canyon floors. Consists of moderately well consolidated, poorly sorted, permeable, commonly slightly dissected gravel, sand, silt, and clay-bearing alluvium Source Kennedy, Michael P., and Siang S. Tan, Geologic Map of the San Diego 30' × 60' Quadrangle, California, California Geological Survey, 2008 Hydrogeology Data regarding depth to groundwater and flow direction for the Site were not readily available. In the absence of Site-specific data, depth to groundwater and flow direction information was reviewed for properties within the Site vicinity using the State Water Resources Control Board GeoTracker database. The following table summarizes the results of this review. Property Location Adjacent to the east of the Site Reported Depth to Groundwater 52.6 to 76.3 feet below grade Reported Groundwater Flow Direction Southwest Source Soil and Groundwater Investigation, Brandywine Distribution Center, 1670 and 1690 Brandywine Avenue, Chula Vista, California, prepared by Ogden Environmental and dated May 1996 Many variables influence depth to groundwater and flow direction and the actual depth to groundwater and flow direction at the Site may be different than presented in this section. Water Quality Survey The following table summarizes the reported water quality in the Site vicinity. Reported Hydrologic Subarea None Reported Hydrologic Area Otay Valley (910.20) Reported Hydrologic Unit Otay (910.00) Reported Beneficial Use Industrial Source California RWQCB, San Diego Region, Water Quality Control Plan for the San Diego Basin, September 8, 1994, with amendments effective prior to May 17, 2016 Phase I Environmental Site Assessment www.scsengineers.com 13 SITE VICINITY RECONNAISSANCE AND OFF-SITE SOURCE SURVEY Current Site Vicinity Conditions The following table summarizes land use and observations in the immediate Site vicinity.vii For the purpose of this Report, the immediate Site vicinity includes those properties judged to be adjacent5 to the Site. Direction Land Use Comments North Mendocino Condominium Complex (1555–1595 Mendocino Drive) (Figure 3g- 2) No obvious indications of the use, storage, or generation of hazardous materials/wastes or petroleum products were observed. East Tecnico Corporation Ship Building & Repair and TransAmerican Manufacturing (1670 Brandywine Avenue) (Figure 3h-1) No obvious indications of the use, storage, or generation of hazardous materials/wastes or petroleum products were observed; however, hazardous materials/wastes are judged likely to be present as discussed in the “Additional SCS Research” section below. Southeast Surgical Specialties Corporation and TForce Logistics Courier (1690 Brandywine Avenue) (Figure 3h-2) South Crash Champions Collision Repair (515 Main Street) Jabil Manufacturer (505 Main Street) (Figure 3h-2) Hazardous materials/wastes or petroleum products use, storage, or generation were observed and are discussed in the “Additional SCS Research” section below. West Single-family residences (512, 514, 515 Tan Oak Court, 516 Timber Street, and 1649–1665 Oleander Avenue) (Figure 3g-1) No obvious indications of the use, storage, or generation of hazardous materials/wastes or petroleum products were observed. Environmental Regulatory Database Report An environmental regulatory database report (Radius Map™ reportviii) was prepared by EDR for the Site. Local, state, and federal regulatory databases were reviewed for the Site and for those facilities within up to 1 mile of the Site. The Radius Map™ report was reported to have been prepared in general accordance with the ASTM standard for the regulatory database review for Phase I Environmental Site Assessments. The locations of the referenced facilities relative to the Site are shown on the overview maps, included in the Radius Map™ report. A description of the various 5 Adjacent is defined by ASTM E1527-13 as any real property or properties the border of which is contiguous or partially contiguous with that of the Site or that would be contiguous or partially contiguous with that of the Site but for a street, road, or other public thoroughfare separating them. Phase I Environmental Site Assessment www.scsengineers.com 14 databases, as well as the date each database was most recently updated, is included in the Radius Map™ report. The Radius Map™ report is included in the Appendices to this Report. Based on a review of the Radius Map™ report, the following table summarizes the facilities within the selected search radii and whether the Site or a facility that was interpreted to be adjacent to the Site was listed on each database. Federal or State Government Database Search Radius Number of Reported Facilities On Site Adjacent to the Site National Priorities List (NPL) 1.00 mile 0 No No NPL Delisted 1.00 mile 0 No No Superfund Enterprise Management System SEMS) 0.50 mile 0 No No No Further Remedial Action Planned NFRAP) 0.50 mile 3 No No Resource Conservation and Recovery Act– Corrective Action (RCRA COR ACT) 1.00 mile 1 No No RCRA Treatment and Disposal Facilities RCRA TSD) 0.50 mile 0 No No RCRA Generators (RCRA GEN) 0.25 mile 10 No Yes Federal Engineering and Institutional Controls (IC/EC) 0.50 mile 0 No No Emergency Response Notification System ERNS) 0.12 mile 0 No No State/Tribal-Equivalent NPL 1.00 mile 0 No No State/Tribal-Equivalent CERCLIS ENVIROSTOR) 1.00 mile 4 No No State/Tribal Solid Waste List (SWL) 0.50 mile 2 No No State/Tribal Leaking Underground Storage Tanks (LUST, San Diego County Site Assessment and Mitigation [SAM], Spills, Leaks, Investigation, and Cleanup [SLIC]) 0.50 mile 11 No Yes State/Tribal Underground/Aboveground Storage Tanks (USTs/ASTs) 0.25 mile 4 No No State/Tribal Voluntary Cleanup Program VCP) 0.50 mile 0 No No Federal Brownfields 0.50 mile 1 No No Phase I Environmental Site Assessment www.scsengineers.com 15 Federal or State Government Database Search Radius Number of Reported Facilities On Site Adjacent to the Site Local Lists of Landfill/Solid Waste Disposal Sites Various 1 No No Local Lists of Hazardous Waste/Contaminated Sites (San Diego HMMD) Various 13 No Yes Local Lists of Registered Storage Tanks Statewide Environmental Evaluation and Planning System [SWEEPS UST], Historic UST, CA Facility Inventory Database [FID] UST) 0.25 mile 7 No No Local Land Records (DEED) 0.50 mile 1 No No Records of Emergency Release Reports 0.001 mile 0 No No Other (RCRA NonGen and CA CIWQS) Various 36 Yes Yes EDR High Risk Historical Records (Historic Auto, Historic Cleaner, Manufactured Gas Plant [MGP]) 0.125 mile 0 No No Exclusive Recovered Government Archines 0.001 mile 0 No No The Site was listed on the following databases: California Integrated Water Quality System (CIWQS) database as 517 Shinohara Lane for storm water construction on the Site in 1994 Regulatory agency files requested for the Site are discussed in the “Site Research” section above. Off-Site facilities listed in the Radius Map™ report were evaluated as to their potential to impact the Site. The databases included in the Radius Map™ report can be grouped into two general categories: databases reporting unauthorized releases of hazardous substances or petroleum products (e.g., LUSTs, RCRA COR ACT facilities, National Priorities List [a.k.a. Superfund] sites) and databases reporting permitted hazardous materials users and hazardous waste generators for which a release has not been reported to, and recorded by, the regulatory agency. SCS evaluated each of the off-Site facilities listed in the Radius Map™ report as to their potential to impact the Site, based on the following factors: Reported distance of the facility from the Site6 6 Based on “Technical Justification for Groundwater Media-Specific Criteria,” (Groundwater Study) (March 2012) developed to support the state of California “Low Threat Closure Policy” (adopted May 2012), “plume length studies recognize that petroleum plumes stabilize in length due to natural attenuation.” The Groundwater Study goes on to cite Shih et al., 2004, that a peer-reviewed study of plume lengths at 500 petroleum UST sites in the Los Angeles area Phase I Environmental Site Assessment www.scsengineers.com 16 The nature of the database on which the facility is listed, and/or whether the facility was listed on a database reporting unauthorized releases of hazardous materials, petroleum products, or hazardous wastes Reported case type (e.g., soil only, failed UST test only) Reported substance released (e.g., chlorinated solvents, gasoline, metals) Reported regulatory agency status (e.g., case closed, “no further action”) Location of the facility with respect to the reported groundwater flow direction and depth to groundwater (discussed in the “Hydrogeology” section of this Report) Based on one or more of the factors listed above, and with possible exceptions discussed in the Additional SCS Research” section below, there is a low likelihood that the off-Site facilities listed in the Radius Map™ report represent a recognized environmental condition in connection with the Site. EDR listed four facilities as being “orphans,” which are facilities for which EDR does not have sufficient information to accurately locate them on a map. Based on a review of the orphans, it is interpreted that none of the facilities are within the requisite search radii for their reported database listings. Additional SCS Research Brandywine Distribution Center/Tap Manufacturing LLC/Transpere, LLC/Keystone Automotive Industries/Jones, Lang, LaSalle Property Management/Lyon Technologies, 1670 & 1690 Brandywine Avenue, Adjacent to the East Based on its listing on the Cleanup Program Sites – Spills, Leaks, Investigations, and Cleanups (CPS- SLIC) and CERS databases and its proximity to the Site (adjacent to the east), the DEH file for this adjacent facility was reviewed. The DEH file includes a soil and groundwater investigation report from May 1996 and Compliance Inspection Reports (CIRs) for the period from 1996 through 2020. In addition, the September 2010 DEH HE-17 database of facilities storing hazardous materials, generating hazardous wastes, and discharging unauthorized releases was reviewed. The following table summarizes information obtained from review of CIRs and the in-house HE-17 database regarding hazardous materials and petroleum products reported to be used and stored, hazardous wastes reported to be generated, and violations of the hazardous waste control law. is widely accepted as representative of plume lengths at California UST sites. Shih et al. reports methyl tertiary butyl ether (MTBE), with 90th percentile maximum plume lengths of 540 feet. Therefore, the detailed review radius for open groundwater cases has been conservatively established by SCS at 0.20 mile (approximately 1,000 feet). For non- release cases (e.g., permitted facilities), only those facilities that were judged to be immediately adjacent to the Site were interpreted to have the potential to represent a recognized environmental condition. Phase I Environmental Site Assessment www.scsengineers.com 17 Year Hazardous Materials, Petroleum Products, Hazardous Waste Violations 1996 to 2002 Paint booth Paint filters (55 gallons) Paint sludge (30 gallons) Organic solids (330 gallons) Inorganic solid waste (3,900 pounds) Paint chips not swept but washed away with water (1999) Paint car outside of paint booth (1999) Disposal to an unauthorized point 1997) 2007 to 2014 Absorbent waste Rags Powder coating dust Sand blasting media dust Scrap metal Used lubricating oil (55 gallons) Accumulated waste too long Missing records 2017 to 2019 Lubricating oil (55 gallons) Plasma quench coolant (55 gallons) Used oil (55 gallons) Used coolant (55 gallons) Acetylene, argon/carbon dioxide mixture, nitrogen, and oxygen (up to 3,900 cubic feet) Propane (8 gallons) Parts washer processing unit (30-gallon capacity) None 2020 Capacitors and ballasts with polychlorinated biphenyls (PCBs) (110 gallons) Laptop batteries (110 gallons) Alkaline batteries (55 gallons) Missing records Inadequate training In 1997, records indicate hazardous waste disposal to an unauthorized point. No additional details were available, although an unauthorized release case was not opened by the DEH at that time. Note that in our experience, disposal violations typically regarded the disposal of minor quantities of paint, used oil, rags, or filters to the ground surface, trash, or sanitary sewer system, and if not opened as unauthorized release cases by the overseeing regulatory agency, typically present a low likelihood of a recognized environmental condition. Overall, based on the reported types and quantities of hazardous materials and waste reported at this facility, and the reported depth to groundwater (approximately 52 to 76 feet below grade), there is a low likelihood that the materials reported on the CIRS database represent a recognized environmental condition to the Site. Omar Rendering facility located at 1886 Auto Park Place (Approximately 1,500 feet to the east) The following reports were included in the DEH file regarding the CPS-SLIC, soil and groundwater investigation, and reviewed as part of this Assessment: Soil and Groundwater Investigation Brandywine Distribution Center, 1670 and 1690 Brandywine Avenue, Chula Vista, California prepared by Ogden Environmental and dated May 1996 Phase I Environmental Site Assessment www.scsengineers.com 18 Annual Report: April 2020 to March 2021, Monitoring and Reporting Program No. R9- 2017-0114 and Cleanup and Abatement Order R9-2003-0080, Waste Management Containment Cell, Former Omar Rendering Site, 1886 Auto Park Place, Chula Vista, CA 91911, prepared by LandBank Properties, LLC and dated April 29, 2021 In March 1994, a Phase I investigation at the property located adjacent to the east of the Site at the Brandywine Distribution Center at 1670 & 1690 Brandywine Avenue found that no regulated or hazardous substances were found to be used or disposed of at the property and that all previous tenants were primarily product distributors. In May 1995, a Phase II was conducted at the same property and results indicated volatile organic compounds (VOCs) were found in the soil near the water table and in the groundwater. In May 1996, groundwater was found to be impacted by VOCs at this east adjacent property. Groundwater results indicated VOCs above laboratory reporting limits, primarily with trichloroethene TCE) at 720 micrograms per liter (ug/L), and also with tetrachloroethene (PCE) at 56 ug/L, and methylene chloride (MEC) at 79 ug/L in MW-04. It was determined that the property was not the source of the pollutants and that the likely source is the former Omar Rendering facility located at 1886 Auto Park Place, a property that stored hazardous waste in evaporation ponds from 1959 to 1978, which were situated to the east and cross- to up-gradient of the Brandywine Distribution Center. The RWQCB closed the case administratively in 2017, noting the Brandywine Distribution Center was not the source of the contamination and that the samples collected at the property suggest a potential threat to indoor air. The RWQCB recommended more recent groundwater data. Omar Rendering facility is approximately 1,500 feet to the east and cross- to up-gradient of the Site and began remediation circa 1980, with removal of the waste ponds and their disposal at a permitted location. In 1981, the impacted soil beneath the waste ponds was placed in a lined and capped waste cell in the northwest corner of the property. Subsequently the waste cell has been maintained and monitored by the RWQCB. In January 2021, during the most recent sampling event at the former Omar Rendering facility, the monitoring well closest to the Site, well MW-18, situated approximately 1,500 feet to the east of the Site, indicated results for TCE at 4.3 ug/L. No additional recent well data was available for wells closer to the Site, to indicate whether or not the TCE plume may still be in the immediate vicinity of or beneath the Site. Based on the concentrations of VOCs at the east adjacent property indicated in 1996 (up to 720 ug/L TCE), the cross- to up-gradient position of the source with respect to the groundwater flow direction to the Site (southwest), that the presence of TCE was reported to be present in the monitoring well closest to the Site from the source in the most recent groundwater monitoring report from January 2021, and that no additional, more recent data is available to indicate whether or not the TCE plume may still be in the immediate vicinity of or beneath the Site, there is a low to moderate likelihood that a recognized environmental condition exists at the Site in connection with the former release from the Omar Rendering facility. Additional assessment (e.g., soil vapor sampling) would be necessary to evaluate the potential associated releases. Phase I Environmental Site Assessment www.scsengineers.com 19 H130637, Nypro San Diego, 505 Main Street, Adjacent to the South Based on its listing on the San Diego County HMMD, CERS HAZWASTE, and CER TANKS databases and its proximity to the Site (adjacent to the south), the DEH file for this adjacent facility was reviewed. The DEH file includes CIRs for the period from 1989 through 2020. In addition, the September 2010 DEH HE-17 database of facilities storing hazardous materials, generating hazardous wastes, and discharging unauthorized releases was reviewed. The following table summarizes information obtained from review of CIRs and the in-house HE-17 database regarding hazardous materials and petroleum products reported to be used and stored, hazardous wastes reported to be generated, and violations of the hazardous waste control law. Year Hazardous Materials, Petroleum Products, Hazardous Waste Violations 1989 None listed Missing records Missing labels 1993 to 1996 Waste & mixed oil (695 gallons) Hydrocarbon solvent waste (120 gallons) Oxygenate solvents (360 gallons) Inorganic solid waste (120 pounds) Organic solids (400 pounds) Unspecified solvent mixture (120 gallons) Ultrathene pellets (10,000 pounds) Polyvinylchloride pellets (300,000 pounds) Copolyester pellets (15,000 pounds) Nylon pellets (15,000 pounds) Acrylic pellets (15,000 pounds) Polycarbonate resin pellets (750,000 pounds) Lead batteries (5,176 pounds) Missing records Open waste containers 1997 to 1999 Waste & mixed oil (695 gallons) Hydrocarbon solvent waste (120 gallons) Oxygenate solvents (360 gallons) Inorganic solid waste (120 pounds) Organic solids (400 pounds) Unspecified solvent mixture (120 gallons) Ultrathene pellets (10,000 pounds) Polyvinylchloride pellets (300,000 pounds) Copolyester pellets (15,000 pounds) Nylon pellets (15,000 pounds) Acrylic pellets (15,000 pounds) Polycarbonate resin pellets (750,000 pounds) Lead batteries (5,176 pounds) Disposal of hazardous waste to an unauthorized point Waste container not kept closed Missing records Inadequate training Phase I Environmental Site Assessment www.scsengineers.com 20 Year Hazardous Materials, Petroleum Products, Hazardous Waste Violations 2001 to 2020 Waste & mixed oil (695 gallons) Hydrocarbon solvent waste (120 gallons) Oxygenate solvents (360 gallons) Inorganic solid waste (120 pounds) Organic solids (400 pounds) Unspecified solvent mixture (120 gallons) Ultrathene pellets (10,000 pounds) Polyvinylchloride pellets (300,000 pounds) Copolyester pellets (15,000 pounds) Nylon pellets (15,000 pounds) Acrylic pellets (15,000 pounds) Polycarbonate resin pellets (750,000 pounds) Lead batteries (5,176 pounds) Failed to make a proper waste determination Accumulated waste for too long Missing labels Container not kept closed In 1997, solvent was observed spilled in a flammable storage cabinet, in 1998 waste oil was observed spilled/leaked on the concrete cooling water pad, and in 1999 disposal of metal shavings was observed to the trash. No additional details were available, although unauthorized release cases were not opened by the DEH at that time. Note that in our experience, disposal violations typically regarded the disposal of minor quantities of paint, used oil, rags, or filters to the ground surface, trash, or sanitary sewer system, and if not opened as unauthorized release cases by the overseeing regulatory agency, typically present a low likelihood of a recognized environmental condition. Based on the minor nature of the disposal violations, the lack of known and reported releases, and the down gradient location of this facility with respect to the reported groundwater flow direction and the Site (i.e., groundwater reported to flow to the southwest), there is a low likelihood that a recognized environmental condition exists at the Site in connection with the listing of this south adjacent facility. H208691, Fuller Ford Collision Center, 515 Main Street, Adjacent to the South Based on its listing on the San Diego County HMMD, CERS HAZWASTE, and CER TANKS databases and its proximity to the Site (adjacent to the south), the DEH file for this adjacent facility was reviewed. The DEH file includes CIRs for the period from 2007 through 2021. In addition, the September 2010 DEH HE-17 database of facilities storing hazardous materials, generating hazardous wastes, and discharging unauthorized releases was reviewed and indicated no files are maintained for the facility. The following table summarizes information obtained from review of CIRs regarding hazardous materials and petroleum products reported to be used and stored, hazardous wastes reported to be generated, and violations of the hazardous waste control law. Phase I Environmental Site Assessment www.scsengineers.com 21 Year Hazardous Materials, Petroleum Products, Hazardous Waste Violations 2007 to 2021 Waste oil (30 gallons) Waste oil filters Waste coolant (55 gallons) Waste sand dust (55 gallons) Water-based paint waste (30 gallons) Solvent-based paint waste (30 gallons) Solid paint waste (60 gallons) Oily absorbent waste (30 gallons) Parts washer Missing records Missing labels Based on the quantities of hazardous materials and petroleum products used and stored and hazardous waste generated at this facility, the down gradient location of this facility with respect to the reported groundwater flow direction and the Site (i.e., groundwater reported to flow to the southwest), the absence of disposal violations, and the lack of known and reported releases, there is a low likelihood that a recognized environmental condition exists at the Site in connection with the this west adjacent facility. California Division of Oil and Gas SCS personnel reviewed the California Division of Oil and Gas Map regarding oil and gas well locations within 1 mile of the Site.ix There were no wells interpreted to be located within a 1-mile radius of the Site. DATA GAPS IN CONNECTION WITH OFF-SITE SOURCES Based on the Site vicinity reconnaissance and off-Site source survey, there are no obvious indications of data gaps in connection with off-Site sources. Findings and Opinions—Off-Site Source Survey Based on the off-Site source survey, several facilities in the Site vicinity were reported to have had releases of hazardous materials/waste or petroleum products. With the possible exception below, it is our opinion that there are no recognized environmental conditions at the Site as a result of known and reported releases of hazardous materials/wastes or petroleum products from an off- Site source. This judgment is based on one or more of the following: the reported regulatory status e.g., case closed), the media affected (e.g., soil contamination only), the distance from the Site, the direction from the Site with respect to the reported groundwater flow direction, and information obtained through a review of County of San Diego Department of Environmental Health files. Omar Rendering facility located at 1886 Auto Park Place (Approximately 1,500 feet to the east) In May 1996, groundwater was found to be impacted by VOCs at the property located adjacent to the east of the Site at the Brandywine Distribution Center at 1670 & 1690 Brandywine Avenue. Groundwater results indicated VOCs above laboratory reporting limits, Phase I Environmental Site Assessment www.scsengineers.com 22 Findings and Opinions—Off-Site Source Survey primarily with TCE at 720 ug/L, and also with PCE at 56 ug/L, and MEC at 79 ug/L in MW- 04. It was determined that the property was not the source of the pollutants and that the likely source is the former Omar Rendering facility located at 1886 Auto Park Place, a property that stored hazardous waste in evaporation ponds from 1959 to 1978, which were situated to the east and cross- to up-gradient of the Brandywine Distribution Center. The RWQCB closed the case administratively in 2017, noting the Brandywine Distribution Center was not the source of the contamination and that the samples collected at the property suggest a potential threat to indoor air. The RWQCB recommended more recent groundwater data. Omar Rendering facility is approximately 1,500 feet to the east and cross to up-gradient of the Site and began remediation circa 1980, with removal of the waste ponds and their disposal at a permitted location. In 1981, the impacted soil beneath the waste ponds was placed in a lined and capped waste cell in the northwest corner of the property. Subsequently the waste cell has been maintained and monitored by the RWQCB. In January 2021, during the most recent sampling event at the former Omar Rendering facility, the monitoring well closest to the Site, well MW-18, situated approximately 1,500 feet to the east of the Site, indicated results for TCE at 4.3 ug/L. No additional recent well data was available for wells closer to the Site, to indicate whether or not the TCE plume may still be in the immediate vicinity of or beneath the Site. Based on the concentrations of VOCs at the east adjacent property indicated in 1996 (up to 720 ug/L TCE), the cross- to up-gradient position of the source with respect to the groundwater flow direction to the Site (southwest), that the presence of TCE was reported to be present in the monitoring well closest to the Site from the source in the most recent groundwater monitoring report from January 2021, and that no additional more recent data is available to indicate whether or not the TCE plume may still be in the immediate vicinity of or beneath the Site, there is a low to moderate likelihood that a recognized environmental condition exists at the Site in connection with the former release from the Omar Rendering facility. Additional assessment (e.g., soil vapor sampling) would be necessary to evaluate the potential associated releases. HISTORICAL LAND USE REVIEW In accordance with the ASTM Standard and AAI rule, numerous reasonably ascertainable standard historical information sources were reviewed, and an attempt was made to interpret the historical Site and Site vicinity land use back to the obvious first developed use of the Site. Historical information was reviewed for current Site address. The following table summarizes the historical resources reviewed as part of this Assessment. Phase I Environmental Site Assessment www.scsengineers.com 23 Resource Source Years Available Aerial Photographs NETR Online http://www.historicaerials.com/ Google Earth 1953, 1964, 1966, 1968, 1971, 1978, 1980, 1981, 1982, 1983, 1985, 1988, 1990, 1994, 1997, 2000, 2003, 2005, 2010, 2014, 2016, 2021 City Directories EDR 1960, 1965, 1971, 1975, 1979, 1982, 1986, 1992, 1995, 2000, 2005, 2010, 2014, 2017 Sanborn Fire Insurance Maps EDR Unmapped area Topographic Maps NETR Online http://www.historicaerials.com/ 1904, 1908, 1911, 1915, 1920, 1928, 1932, 1941, 1943, 1955, 1960, 1962, 1977, 2002, 2012, 2015, 2018 Previous Environmental Report Not applicable Discussed in the “Review of Client-Provided Documents” section above Interviews Not applicable Discussed in the “Interviews” section above Historical Site Land Use The following table provides a chronology of the apparent historical Site land uses, as interpreted from a review of information from the sources referenced. Year Interpreted Site Tenants Interpreted Site Use 1904 to 1991 Vacant, undeveloped land None 1993 to 2021 Vacant, undeveloped land, with the northern portion of the Site as graded land, with concrete drainage channels in portions of the Site None Because many of the dates listed above are based on a limited selection of historical resources, they are considered to be approximations only; the actual beginning/ending dates for many of the Site uses listed above may have been earlier or later than indicated. No obvious historical facilities, features of concern, or land uses indicative of the use, storage, or generation of hazardous materials/wastes or petroleum products were found in the historical resources reviewed. Phase I Environmental Site Assessment www.scsengineers.com 24 Historical Site Vicinity Land Use The following table provides a chronology of the apparent historical Site vicinity land uses as interpreted from a review of information from the sources referenced. Years Interpreted Site Vicinity Tenants Interpreted Site Vicinity Use 1555–1595 Mendocino Drive (North) 1904 to 1971 Vacant, undeveloped land None 1975 to 2021 Mendocino Residential Condominium Complex Multi-family residence 1670 Brandywine Avenue (East) 1904 to 1964 Vacant, undeveloped land None 1966 to 1987 Agricultural land Agricultural 1988 to 2021 Various industrial tenants: Icore, USA Discounters, VSE Corp, RayChem Corporation, Hardwoods Inc., Nobel Floral, Grainger, Tecnico, and TransAmerican Industrial 1690 Brandywine Avenue (Southeast) 1904 to 1964 Vacant, undeveloped land None 1966 to 1987 Agricultural land Agricultural 1988 to 2021 Various industrial tenants: General Textiles, Family Bargain Center Stores, Best Buy Wholesale, Lyon Electronic, Lloyd Johnson Company, Bee International, Surgical Specialties, TForce Logistics Industrial 505 & 515 Main Street (South) 1904 to 1950 Vacant, undeveloped land None 1953 to 1970 Greenhouses Agricultural 1975 to 1979 Vacant, graded land None 1985 to 2021 Various industrial tenants: Nypro Inc., Foot Point, Hamilton Meats, Shoe Magoo LLC, South Frames, Fuller Collision Center, Crash Champions Collision Repair, Jabil Manufacturer Industrial Phase I Environmental Site Assessment www.scsengineers.com 25 Years Interpreted Site Vicinity Tenants Interpreted Site Vicinity Use 512, 514, 515 Tan Oak Court, 516 Timber Street, 1649, 1651, 1655, 1657, 1661, 1665 Oleander Avenue (West) 1904 to 1964 Vacant, undeveloped land None 1966 to 2021 Various single-family residential tenants Single-family residential Because many of the dates listed above are based on a limited selection of historical resources, they are considered to be approximations only; the actual beginning/ending dates for many of the Site vicinity uses/development described above may have been earlier or later than indicated. With the possible exceptions described in the “Additional Research” section above and also below, no obvious historical facilities, features of concern, or land uses indicative of the use, storage, or generation of hazardous materials/wastes or petroleum products were found in the historical resources reviewed. Historical Adjacent Agricultural A review of aerial photographs revealed that some type of agricultural activity took place within the Site vicinity between 1966 and 1987. The agricultural activity is interpreted to have possibly taken place at the time that organochlorine pesticides (e.g., DDT and chlordane), toxic metals, and others were in wide general use. These classes of pesticides are known to have the potential to remain in detectable concentrations in the surface for extended periods of time. Based on the interpreted land use of these adjacent properties, SCS’ experience with agricultural properties, and a review of the available literature, it is SCS’ judgment that it is likely that trace concentrations of organochlorine or metallic pesticides are present in the soil at these adjacent properties as a result of the interpreted agricultural land use. It is also SCS’ experience that trace concentrations are likely to be present even in cases of mass grading and earth movement. However, it has generally been SCS’ experience that unless a pesticide mixing, storage, or disposal area was present, concentrations of organochlorine pesticides in the subsurface in general agricultural areas tend to be low. No such areas were reported or are known to have existed at these adjacent properties. Based on SCS’ experience, there is a moderate likelihood that residual concentrations of organochlorine- and metal-based pesticides are present in the shallow surface soil beneath the adjacent properties. Assuming the legal and permitted application of theses pesticides, and assuming existing land use remains the same, this common occurrence is, in SCS’ experience, unlikely to lead to an enforcement action and is therefore likely to be considered de minimis, as defined by ASTM. Based on the fact that Site was not interpreted to have been used for agricultural purposes and the lack of known or reported releases, as well as the down- to cross-gradient topographic location of these facilities with respect to the Site, there is a low likelihood that an adverse environmental condition exists at the Site as a result of the historical agricultural land use at adjacent properties. Phase I Environmental Site Assessment www.scsengineers.com 26 DATA GAPS IN CONNECTION WITH THE HISTORICAL SITE LAND USE Based on a review of historical sources, and with the possible exceptions below, there are no obvious indications of data gaps in connection with the historical Site and Site vicinity land use. Readily available historical information was limited, and information was not available that would provide 5-year data intervals between the following years: 1920 and 1928, 1932 and 1941, 1943 and 1953. Based on the corroborating data from the historical information reviewed (i.e., the Site was interpreted to have been vacant, undeveloped land in each of these years), SCS judged it likely that the historical Site land use during this time period was not significantly different from the interpretation presented in the table above. Findings and Opinions—Historical Site and Site Vicinity Land Use Based on a review of historical resources, it is our opinion that there are no recognized environmental conditions at the Site as a result of a release of hazardous materials/wastes or petroleum products from a known or interpreted historical Site or Site vicinity land use. 5 CONCLUSIONS AND RECOMMENDATIONS SCS has performed an Assessment of 517 Shinohara Lane, Chula Vista, California 91911 (Site), in general conformance with the ASTM Standard Practice for Phase I Environmental Site Assessment Process E 1527-13 and the EPA, 40 CFR 312, Standards and Practices for All Appropriate Inquiries, Final Rule (AAI). Any exceptions to, or deletions from, the ASTM and AAI Scope of Work were previously described in this Report where applicable. With the possible exception below, this Assessment has revealed no evidence of a recognized environmental condition in connection with the Site. Omar Rendering facility located at 1886 Auto Park Place (Approximately 1,500 feet to the east) In May 1996, groundwater was found to be impacted by volatile organic compounds (VOCs) at the property located adjacent to the east of the Site at the Brandywine Distribution Center at 1670 & 1690 Brandywine Avenue. Groundwater results indicated VOCs above laboratory reporting limits, primarily with trichloroethene (TCE) at 720 micrograms per liter (ug/L), and also with tetrachloroethene (PCE) at 56 ug/L, and methylene chloride (MEC) at 79 ug/L in MW-04. It was determined that the property was not the source of the pollutants and that the likely source is the former Omar Rendering facility located at 1886 Auto Park Place, a property that stored hazardous waste in evaporation ponds from 1959 to 1978, which were situated to the east and cross- to up-gradient of the Brandywine Distribution Center. The Regional Water Quality Control Board (RWQCB) closed the case administratively in 2017, noting the Brandywine Distribution Center was not the source of the contamination and that the samples collected at the property suggest a potential threat to indoor air. The RWQCB recommended more recent groundwater data. Phase I Environmental Site Assessment www.scsengineers.com 27 Omar Rendering facility is approximately 1,500 feet to the east and cross- to up-gradient of the Site and began remediation circa 1980, with removal of the waste ponds and their disposal at a permitted location. In 1981, the impacted soil beneath the waste ponds was placed in a lined and capped waste cell in the northwest corner of the property. Subsequently the waste cell has been maintained and monitored by the RWQCB. In January 2021, during the most recent sampling event at the former Omar Rendering facility, the monitoring well closest to the Site, well MW-18, situated approximately 1,500 feet to the east of the Site, indicated results for TCE at 4.3 ug/L. No additional recent well data was available for wells closer to the Site, to indicate whether or not the TCE plume may still be in the immediate vicinity of or beneath the Site. Based on the concentrations of VOCs at the east adjacent property indicated in 1996 (up to 720 ug/L TCE), the cross- to up-gradient position of the source with respect to the groundwater flow direction to the Site (southwest), that the presence of TCE was reported to be present in the monitoring well closest to the Site from the source in the most recent groundwater monitoring report from January 2021, and that no additional, more recent data is available to indicate whether or not the TCE plume may still be in the immediate vicinity of or beneath the Site, there is a low to moderate likelihood that a recognized environmental condition exists at the Site in connection with the former release from the Omar Rendering facility. Additional assessment (e.g., soil vapor sampling) would be necessary to evaluate the potential associated releases. This Assessment has been conducted by an environmental professional whose qualifications7 were made known to the Client. The conclusions and recommendations presented above are based on the review of readily available data obtained as part of this Assessment, current regulatory guidelines, the Site and Site vicinity reconnaissance, and SCS’ experience. 6 REPORT USAGE AND FUTURE SITE CONDITIONS This Report is intended for the sole usage of the Client and other parties designated by SCS. The methodology used during this Assessment was in general conformance with the requirements of the Client and the specifications and limitations presented in the Consulting Agreement (Contract) between the Client and SCS. This Report contains information from a variety of public and other sources, and SCS makes no representation or warranty about the accuracy, reliability, suitability, or completeness of the information. Any use of this Report, whether by the Client or by a third party, shall be subject to the provisions of the Contract between the Client and SCS. Any misuse of or reliance upon the Report shall be without risk or liability to SCS. Assessments are qualitative, not comprehensive, in nature and may not identify all environmental problems or eliminate all risk. For every property, but especially for properties in older downtown or urban areas, it is possible for there to be unknown, unreported recognized environmental conditions, USTs, or other features of concern that might become apparent through demolition, construction, or excavation activities, etc. In addition, the scope of services for this project was limited to those items 7 SCS declares that, to the best of its professional knowledge and belief, the reviewer meets the definition of Environmental Professional as defined in section 312.10 of 40 CFR 312 and has the specific qualifications based on education, training, and experience to assess a property of the nature, history, and setting of the subject property. SCS has developed and performed All Appropriate Inquiries in conformance with the standards and practices set forth in 40 CFR 312. The qualifications of the report preparers are included in the Appendices. Phase I Environmental Site Assessment www.scsengineers.com 28 specifically named in the scope of services for this Report. Environmental issues not specifically addressed in the scope of services for this project are not included in this Report. Land use, condition of the properties within the Site, and other factors may change over time. The information and conclusions of this Report are judged to have been relevant at the time the work described in this Report was conducted. This Report should not be relied upon to represent future Site conditions unless a qualified consultant familiar with the practice of Phase I Environmental Site Assessments in the County of San Diego is consulted to assess the necessity of updating this Report. The property owners at the Site are solely responsible for notifying all governmental agencies and the public of the existence, release, or disposal of any hazardous materials/wastes or petroleum products at the Site, whether before, during, or after the performance of SCS’ services. SCS assumes no responsibility or liability for any claim, loss of property value, damage, or injury that results from hazardous materials/wastes or petroleum products being present or encountered within the Site. Although this Assessment has attempted to assess the likelihood that the Site has been impacted by a hazardous material/waste release, potential sources of impact may have escaped detection for reasons that include, but are not limited to, (1) inadequate or inaccurate information rightfully provided to SCS by third parties, such as public agencies and other outside sources; (2) the limited scope of this Assessment; and (3) the presence of undetected, unknown, or unreported environmental releases. 7 LIKELIHOOD STATEMENTS Statements of “likelihood” have been made in this report. Likelihood statements are based on professional judgments of SCS. The term “likelihood,” as used herein, pertains to the probability of a match between the prediction for an event and its actual occurrence. The likelihood statement assigns a measure for a “degree of belief” for the match between the prediction for the event and the actual occurrence of the event. The likelihood statements in this Report are made qualitatively (expressed in words). The qualitative terms can be approximately related to quantitative percentages. The term “low likelihood” is used by SCS to approximate a range of 10 to 20 percent; the term “moderate likelihood” refers to an approximate range of 40 to 60 percent; and the term “high likelihood” refers to an approximate range of 80 to 90 percent. 8 SPECIAL CONTRACTUAL CONDITIONS BETWEEN USER AND ENVIRONMENTAL PROFESSIONAL There were no special contractual conditions between the user of this Assessment, the environmental professional, and SCS. 9 ENDNOTES i Site reconnaissance conducted by Allison O’Neal (SCS) on July 1, 2021. ii Records request—County of San Diego Department of Environmental Health by Allison O’Neal SCS) on June 23, 2021. Phase I Environmental Site Assessment www.scsengineers.com 29 iii Records request—City of Chula Vista Fire Department by Allison O’Neal (SCS) on June 23, 2021. iv Records request—San Diego County Air Pollution Control District (SDAPCD) by Allison O’Neal on June 23, 2021. v Records request—City of Chula Vista Industrial Waste Program by Allison O’Neal on June 23, 2021. vi Records request—San Diego Regional Water Quality Control Board (RWQCB) by Allison O’Neal on June 23, 2021. vii Site vicinity reconnaissance conducted by Allison O’Neal (SCS) on July 1, 2021. viii EDR, “Radius Map™ Report,” unpublished report prepared for 517 Shinohara Lane, dated June 24, 2021. ix California Division of Oil, Gas, and Geothermal Resources Online Mapping System, http://maps.conservation.ca.gov/doms/doms-app.html. FIGURES North(Not toscale)Disclaimer: This figure is based on available data. Actualconditions may differ. Alllocations anddimensionsareapproximate.FOUR- WAY SITE LOCATION MAPVWP-OP Shinohara Owner, LLC517 Shinohara LaneChula Vista, CaliforniaReference: U.S.G.S. 7.5 Minute Quadrangle MapImperial Beach, CaliforniaReference:U.S.G.S. Figure 2Project No.: 01221156.01Disclaimer: This figure is based on available data. Actualconditions may differ. All locations and dimensions are approximate.SITE AND SITE VICINITY PLANVWP-OP Shinohara Owner, LLC517 Shinohara LaneChula Vista, CaliforniaDateDrafted:7/2/21NorthNot to ScaleS C S E N G I N E ERSEnvironmental Consultants8799 Balboa Avenue, Suite 290San Diego, California 92123Reference: Google Earth Aerial PhotographChula Vista, California - December 20201555 to 1595 Mendocino Drive(Mendocino Condominium Complex)1555 to 1595 Mendocino Drive(Mendocino Condominium Complex)1555 to 1595 Mendocino Drive(Mendocino CondominiumComplex) PHOTOGRAPHIC PLATE VWP-OP Shinohara Owner, LLC 517 Shinohara Lane Chula Vista, California Project No.: 01221156.01 Date Drafted: 7/3/21 S C S E N G I N E E R S Environmental Consultants 8799 Balboa Avenue, Suite 290 San Diego, California 92123 2) View of the Site looking northwest. 1) View of the southeast entrance to the Site. Figure 3a PHOTOGRAPHIC PLATE VWP-OP Shinohara Owner, LLC 517 Shinohara Lane Chula Vista, California Project No.: 01221156.01 Date Drafted: 7/3/21 S C S E N G I N E E R S Environmental Consultants 8799 Balboa Avenue, Suite 290 San Diego, California 92123 2) View of the Site looking northeast. 1) View of the Site looking north. Figure 3b PHOTOGRAPHIC PLATE VWP-OP Shinohara Owner, LLC 517 Shinohara Lane Chula Vista, California Project No.: 01221156.01 Date Drafted: 7/3/21 S C S E N G I N E E R S Environmental Consultants 8799 Balboa Avenue, Suite 290 San Diego, California 92123 2) View of the Site looking southeast. 1) View of the central portion of the Site looking east. Figure 3c PHOTOGRAPHIC PLATE VWP-OP Shinohara Owner, LLC 517 Shinohara Lane Chula Vista, California Project No.: 01221156.01 Date Drafted: 7/3/21 S C S E N G I N E E R S Environmental Consultants 8799 Balboa Avenue, Suite 290 San Diego, California 92123 2) View of the Site looking southwest. 1) View of the Site looking south. Figure 3d PHOTOGRAPHIC PLATE VWP-OP Shinohara Owner, LLC 517 Shinohara Lane Chula Vista, California Project No.: 01221156.01 Date Drafted: 7/3/21 S C S E N G I N E E R S Environmental Consultants 8799 Balboa Avenue, Suite 290 San Diego, California 92123 2) View of typical debris pile observed on Site. 1) View of the concrete drainage in the northwest portion of the Site. Figure 3e PHOTOGRAPHIC PLATE VWP-OP Shinohara Owner, LLC 517 Shinohara Lane Chula Vista, California Project No.: 01221156.01 Date Drafted: 7/3/21 S C S E N G I N E E R S Environmental Consultants 8799 Balboa Avenue, Suite 290 San Diego, California 92123 2) View of the roadway and concrete drainage in the east portion of the Site. 1) View of the northern portion of the Site, looking north. Figure 3f PHOTOGRAPHIC PLATE VWP-OP Shinohara Owner, LLC 517 Shinohara Lane Chula Vista, California Project No.: 01221156.01 Date Drafted: 7/3/21 S C S E N G I N E E R S Environmental Consultants 8799 Balboa Avenue, Suite 290 San Diego, California 92123 2) View of the adjacent properties to the north of the Site. 1) View of the adjacent properties to the west of the Site. Figure 3g PHOTOGRAPHIC PLATE VWP-OP Shinohara Owner, LLC 517 Shinohara Lane Chula Vista, California Project No.: 01221156.01 Date Drafted: 7/3/21 S C S E N G I N E E R S Environmental Consultants 8799 Balboa Avenue, Suite 290 San Diego, California 92123 2) View of the adjacent properties to the south and southeast of the Site. 1) View of the adjacent property to the east of the Site. Figure 3h APPENDICES 1 Revised December 7, 2012 GLOSSARY adjacent property. Any real property or properties the border of which is contiguous or partially contiguous with that of the Site or that would be contiguous or partially contiguous with that of the Site but for a street, road, or other public thoroughfare separating them. aerial photographs. Photographs taken from an airplane or helicopter of areas encompassing the Site. asbestos. Six naturally occurring fibrous minerals found in certain types of rock formations. Of the six, the minerals chrysotile, amosite, and crocidolite have been the most commonly used in building products. When inhaled in sufficient quantities, asbestos fibers can cause serious health problems. asbestos-containing material (ACM). Any material or product that contains more than 1% asbestos. construction debris. Any concrete, brick, asphalt, and other building materials discarded in the construction of a building or other improvement to property. Controlled recognized environmental conditions. A recognized environmental condition resulting from a past release of hazardous substances or petroleum products that has been addressed to the satisfaction of the applicable regulatory authority (for example, as evidenced by the issuance of a no further action letter or equivalent, or meeting risk-based criteria established by regulatory authority), with hazardous substances or petroleum products allowed to remain in place subject to the implementation of required controls (for example, property use restrictions, activity use limitations, institutional controls, or engineering controls). de minimis condition. A condition that generally does not present a threat to human health or the environment and that generally would not be subject to an enforcement action if brought to the attention of appropriate governmental agencies). A condition considered de minimis is not a recognized environmental condition. drum. A container (typically, but not necessarily, holding 55 gallons of liquid) that may be used to store hazardous substances or petroleum products. dry well. Underground areas where soil has been removed and replaced with pea gravel, coarse sand, or large rocks. Dry wells are used for drainage, to control storm runoff, for the collection of spilled liquids (spilled intentionally or not), and for wastewater disposal (often illegal). fill dirt. Dirt, soil, sand, or other earth that is obtained off site and that is used to fill holes or depressions, create mounds, or otherwise artificially change the grade or elevation of real property. It does not include material that is used in limited quantities for normal landscaping activities. fire insurance map. Maps produced for private fire insurance map companies that indicate uses of properties at specified dates and that encompass the property. hazardous material. Any material that, because of its quantity, concentration, or physical and chemical characteristics, poses a significant present or potential hazard to human health and safety or to the environment if released into the workplace or the environment. Hazardous materials include, but are not limited to, hazardous substances, hazardous waste, and any material which a handler or the administering agency has a reasonable basis for believing would be injurious to the health or safety of persons or harmful to the environment if released into the workplace or the environment. hazardous substance. Pursuant to CERCLA, hazardous substances include the following: 2 Revised December 7, 2012 1) All toxic pollutants and hazardous substances listed under the Clean Water Act 2) Hazardous wastes regulated under RCRA 3) Any hazardous air pollutant under the Clean Air Act 4) Chemicals designated as “immediately hazardous” under the Toxic Substance Control Act The EPA is also allowed to designate additional substances as hazardous if they present a substantial danger to the public health or welfare or the environment when released. hazardous waste. A substance defined pursuant to the Solid Waste Disposal Act amended by RCRA, a hazardous waste is a solid waste, or a combination of solid wastes, which because of its quantity, concentration, or physical, chemical, or infectious characteristics, may contribute to an increase in mortality or an increase in serious irreversible, or incapacitating illness or pose a substantial present or potential hazard to human health or the environment when improperly treated, stored, transported, or disposed of, or otherwise managed. historical recognized environmental condition. A past release of any hazardous substances or petroleum products that has occurred in connection with the property and has been addressed to the satisfaction of the applicable regulatory authority or meeting unrestricted use criteria established by a regulatory authority, without subjecting the property to any required controls (for example, property use restrictions, activity and use limitations, institutional controls, or engineering controls). landfill. A place or area of land used for the disposal of solid wastes as defined by state solid waste regulations. Synonymous with the term solid waste disposal site, a landfill is also known as a garbage dump or trash dump. likelihood. As used in this Report, the term likelihood pertains to the probability of a match between the prediction of an event and its actual occurrence. As used by SCS Engineers, the term low likelihood approximates a percentage range to 10 to 20 percent; moderate likelihood approximates 40 to 60 percent; and high likelihood approximates 80 to 90 percent. Material Safety Data Sheet (MSDS). Written or printed material concerning a hazardous substance which is prepared by chemical manufacturers, importers, and employers for hazardous chemicals pursuant to OSHA standards. obvious. That which is plain or evident. The term refers to a condition or fact that could not be ignored or overlooked by a reasonable observer while physically observing the property. PCE. Perchloroethene/perchloroethylene, or “Perc”; also tetrachloroethene/tetrachloroethylene; commonly used as a solvent for dry-cleaning. petroleum products. Petroleum, including crude oil, natural gas, natural gas liquids, liquefied natural gas, synthetic gas usable for fuel, kerosene, diesel oil, jet fuels, motor oil, hydraulic oil, gear oils, and fuel oil. recognized environmental conditions (RECs). Recognized environmental conditions, as defined by the American Society for Testing and Materials (ASTM), include the presence or likely presence of any hazardous substances or petroleum products in, on, or at a property: (1) due to any release to the environment; (2) under conditions indicative of a release to the environment; or (3) under conditions that pose a material threat of a future release to the environment. However, the term is 3 Revised December 7, 2012 not intended to include de minimis conditions. retail quantities (RQs). Quantities of hazardous materials usually less than 50 gallons, 100 pounds, or 200 cubic feet of gas (under the regulatory reporting limits). small retail quantities (SRQs). Quantities of hazardous materials in containers of 5 gallons or less, and less than 50 gallons in aggregate. solvent. A chemical compound that is capable of dissolving another substance and is itself a hazardous substance, such as TCE, TCA, PCE, Stoddard solvent, paint thinner, mineral spirits, and acetone. Solvents are used in a number of manufacturing or industrial processes. TCA. Trichloroethane; also 1,1,1 TCA; a commonly used industrial solvent for degreasing/cleaning. underground storage tank (UST). Any tank, including underground piping connected to the tank, that is or has been used to contain hazardous substances or petroleum products and the volume of which is 10 percent or more beneath the surface of the ground. visually and/or physically observed. This term refers to observations made by vision during the Site visit while walking through the Site or Site building(s), and observations made by the sense of smell, particularly awareness of noxious or foul odors. ACRONYMS g/kg micrograms per kilogram g/L micrograms per liter ARAR Applicable, Relevant, and Appropriate Requirements ASPIS Abandoned Sites Program Information System APCD Air Pollution Control District ASHRAE American Society of Heating, Refrigerating and Air-Conditioning Engineers AST aboveground storage tank ASTM American Society for Testing and Materials BAT Best Available Technology bg below grade bgs below ground surface BMP Best Management Practice BTEX benzene, toluene, ethylbenzene, and xylenes Cal-EPA California Environmental Protection Agency CCDC Centre City Development Corporation CCR California Code of Regulations CEQA California Environmental Quality Act CERCLA Comprehensive Environmental Response, Compensation, and Liability Act of 1980 CGI Combustible Gas Indicator CHSP Community Health and Safety Plan CIR Compliance Inspection Report 4 Revised December 7, 2012 CoCs Constituents of Concern CPT Cone Penetration Testing CREC Controlled Recognized Environmental Condition DAF Dilution and Attenuation Factor DDT Dichlorodiphenyltrichloroethane DEED RSTR California Department of Health Services Deed Restriction DEH County of San Diego Department of Environmental Health DTSC Department of Toxic Substance Control EPA Environmental Protection Agency ERNS Emergency Response Notification System ESA Environmental Site Assessment FoPC Features of Potential Concern HREC Historical Recognized Environmental Condition HMMD Hazardous Materials Management Division, County of San Diego HVAC heating, ventilation, and air conditioning HVOCs halogenated volatile organic compounds HWSSL Hazardous Waste and Substances Sites List IDW investigation-derived wastes IPM integrated pest management JURMP Jurisdictional Urban Runoff Management Program LEL lower explosive limit LESA Limited Environmental Site Assessment LNAPL Light Nonaqueous Phase Liquid LOA Letter of Authorization LUFT leaking underground fuel tank LUST leaking underground storage tank mg/kg milligrams per kilogram MIWD Metropolitan Industrial Wastewater Division MSCP Multiple Species Conservation Plan MSDS Material Safety Data Sheet MTBE methyl tertiary butyl ether; also methyl tert-butyl ether NA not applicable NCP National Contingency Plan ND not detected NESSHAPS National Emissions Standards for Hazardous Air Pollutants NFA no further action NFRAP No Further Remedial Action Plan NOI Notice of Intent 5 Revised December 7, 2012 NPDES National Pollutant Discharge Elimination System NPL National Priorities List OLS ordinary least squared OSHA Occupational Safety and Health Administration PCBs polychlorinated biphenyls PCE perchloroethene/perchloroethylene, or “Perc”; also tetrachloroethene/tetrachloroethylene PEAR Preliminary Environmental Assessments Required PID photoionization detector PMP Property Mitigation Plan PAHs polynuclear aromatic hydrocarbons PRG Preliminary Remediation Goals PRP potentially responsible party (pursuant to CERCLA) PSH phase-separated hydrocarbons QAPP Quality Assurance Project Plan RCRA Resource Conservation and Recovery Act RCRA VIOL Comprehensive Environmental Response, Compensation and Liability Act–hazardous waste generators violations/enforcement actions RCRIS-G Comprehensive Environmental Response, Compensation, and Liability Act Information System–Generators (hazardous waste) REC recognized environmental condition RF remote fill RNA remediation by natural attenuation RQs retail quantities RWQCB Regional Water Quality Control Board SAM Site Assessment and Mitigation Program (San Diego County Department of Environmental Health) SAP Site Assessment Protocol SCL Department of Toxic Substance Control database SDG&E San Diego Gas and Electric SI site inspection SRQs small retail quantities SMP Soil Management Plan SPCC Spill Prevention Control and Countermeasure STLC Soluble Threshold Limit Concentration SWAT Solid Waste Assessment Test SWIS Solid Waste Information System SWLF Solid Waste Landfills SWPPP Storm Water Pollution Prevention Plan SWRCB State Water Resources Control Board TCA Trichloroethane; also 1,1,1 TCA 6 Revised December 7, 2012 TCE trichloroethene; trichloroethylene TCLP Toxicity Characteristic Leaching Procedure THF Tetrahydrofuran TPH total petroleum hydrocarbons TPHg TPH as gasoline TPHd TPH as diesel TPHext TPH extended range TPHo TPH oil range TRIS Toxic Release Information System TRPH total recoverable petroleum hydrocarbons TTLCs Total Threshold Limit Concentrations UAR unauthorized release USGS United States Geological Survey UST underground storage tank VAP Voluntary Action Plan VES Vapor Extraction System WDR Waste Discharge Requirements WET Waste Extraction Test WMUDS Waste Management Unit Database System COUNTY OF SAN DIEGO DEPARTMENT OF ENVIRONMENTAL HEALTH RECORDS FOR THE SITE DEH-9098 (Rev. 11/17) Request # County of San Diego DEPARTMENT OF ENVIRONMENTAL HEALTH P.O. BOX 129261, SAN DIEGO, CA 92112-9261 858) 505-6700 FAX (858) 505-6848 www.sdcdeh.org PUBLIC RECORDS REQUEST FOR THE SITE ASSESSMENT AND MITIGATION (SAM) PROGRAM AND HAZARDOUS MATERIALS DIVISION (HMD) Requestor Name: Allison O’Neal E-Mail: aoneal@scsengineers.com Phone: (858)583-7763 FAX: ( ) Company Name: SCS Engineers Mailing Address: 8799 Balboa Ave #290 San Diego CA, 92123 You may attach a business card/overprint with business card if preferred) Additional information may be accessed from the DEH website, www.sdcdeh.org. Fax or email your completed form to the Public Records Program at (858) 505-6848 or PublicRecords.DEH@sdcounty.ca.gov. The following information is required. Separate forms are needed for each address or parcel number. 517 Shinohara Lane, Chula Vista, CA 91911 or 644-040-01 Exact Address (Street, City and Zip Code) Assessor Parcel Number Optional information (establishment permit number, business name, etc.): Please indicate the purpose of your search by checking all that apply: X Contaminated Property Investigation(s) (SAM Cases) X SAM Closure Letter/Report X Hazardous Materials Permit & Underground Storage Tank Files ( HMD/UST) Other (specify): X Monitoring Well Files OFFICE USE ONLY BELOW THIS LINE Files reviewed by: of Date: Files copied for: of Date: Request cancelled by: Date: Photocopies Cost E-mailed / picked up / mailed on By A search for DEH records checked above has been conducted and the following apply: SAM files for the permit number(s) listed below are available. HMD/UST files for the permit number(s) listed below are available. LMWP files for the permit number(s) listed below are available. No SAM/HMD/UST records were found / purged for the address/APN you requested. Signature - DEH Representative Date DEH complies fully with the California Public Records Act and the Federal Freedom of Information Act. Please be advised that photocopy and/or scanned file fees may apply. 06-472/06-473 Rcvd 06/23/2021 06/23/202106-472 > 06-491 e-mail 06/24/2021 - 06-472> 06-491 - ECA CLIENT-PROVIDED DOCUMENTS PHASE I ENVIRONMENTAL SITE ASSESSMENT REPORT Industrial Land 517 Shinohara Lane Chula Vista, California 91911 Report Date: January 16, 2018 Partner Project No. 17-199602.1 Prepared for: STOS Partners 669 2nd Street Encinitas, California 92024 2154 Torrance Blvd., Suite 200, Torrance, CA 90501 Phone 800-419-4923 Fax 866-928-7418 January 16, 2018 Mr. CJ Stos STOS Partners 669 2nd Street Encinitas, California 92024 Subject: Phase I Environmental Site Assessment Industrial Land 517 Shinohara Lane Chula Vista, California 91911 Partner Project No. 17-199602.1 Dear Mr. Stos: Partner Engineering and Science, Inc. (Partner) is pleased to provide the results of the Phase I Environmental Site Assessment (Phase I ESA) report of the abovementioned address (the “subject property”). This assessment was performed in general conformance with the scope and limitations as detailed in the ASTM Practice E1527-13 Standard Practice for Environmental Site Assessments: Phase I Environmental Site Assessment Process. This assessment included a site reconnaissance as well as research and interviews with representatives of the public, property ownership, site manager, and regulatory agencies. An assessment was made, conclusions stated, and recommendations outlined. We appreciate the opportunity to provide environmental services to you. If you have any questions concerning this report, or if we can assist you in any other matter, please contact me at (619) 925-9672 or MLambson@partneresi.com. Sincerely, DRAFT Mark Lambson Principal Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page i EXECUTIVE SUMMARY Partner Engineering and Science, Inc. (Partner) has performed a Phase I Environmental Site Assessment ESA) in general accordance with the scope of work and limitations of ASTM Standard Practice E1527-13, the Environmental Protection Agency Standards and Practices for All Appropriate Inquiries (AAI) (40 CFR Part 312) and set forth by STOS Partners for the property located at 517 Shinohara Lane in the City of Chula Vista, San Diego County, California (the “subject property”). The Phase I Environmental Site Assessment is designed to provide STOS Partners with an assessment concerning environmental conditions (limited to those issues identified in the report) as they exist at the subject property. Property Description The subject property is located at the western terminus of Shinohara Lane, approximately 350 feet west of Brandywine Avenue within a mixed commercial, industrial, and residential area of San Diego County. Please refer to the table below for further description of the subject property: Subject Property Data Address: 517 Shinohara Lane, Chula Vista, California Property Use: Vacant Land Acreage (Ac): 9.56 Ac Number of Buildings: 0 Number of Floors: Not applicable Gross Building Area (SF): Not applicable Net Rentable Area (SF): Not applicable Date of Construction: Not applicable Assessor’s Parcel Number (APN): 644-040-01-00 Type of Construction: Not applicable Current Tenants: Not applicable Site Assessment Performed By: Sara A. Gengler of Partner Site Assessment Conducted On: January 2, 2018 The subject property is currently vacant land occupied by no tenants. No operations are conducted on site. According to available historical sources, the subject property was formerly undeveloped as early 1904. No tenants have occupied the subject property. The immediately surrounding properties consist of a residential condominium complex to the north; a multi-unit light industrial building and Fuller Collision Center to the south; two multi-unit light industrial buildings and Shinohara Lane to the east; and a single-family residential community to the west. According to a previous subsurface investigation conducted at the east adjacent sites, the depth and direction of groundwater in the vicinity of the subject property is inferred to be approximately 45 to 85 feet below ground surface (bgs) and flows toward the southwest. Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page ii Findings A recognized environmental condition (REC) refers to the presence or likely presence of any hazardous substances or petroleum products in, on, or at a property: due to release to the environment; under conditions indicative of a release to the environment; or under conditions that pose a material threat of a future release to the environment. The following was identified during the course of this assessment: x Based on subsurface investigations conducted at the east adjacent Brandywine Distribution Center sites, it appears that chlorinated hydrocarbons (TCE reported at concentrations of 1 l to 720 l) potentially originating from the up-gradient former Omar Rendering site and the Otay Landfill have impacted the groundwater at the east adjacent Brandywine Distribution Center sites, and the potential exists that chlorinated hydrocarbons originating from the former Omar Rendering site and the Otay Landfill have impacted the subsurface of the subject property. The Regional Water Quality Control Board (RWQCB), the lead oversight agency, reviewed a 1996 Soil and Groundwater Investigation report for the Brandywine Distribution Center case and in a letter dated November 15, 1996, summarized that volatile organic compounds (VOC) including trichloroethene (TCE), tetrachloroethene (PCE), and methylene chloride (MEC) had been discovered at elevated concentrations in groundwater beneath the sites, but not in the unsaturated soil zone. Even though the RWQCB cited that the former Omar Rendering site and the former Otay Landfill had not been clearly identified as the sources of impacted groundwater beneath the Brandywine Distribution Center, the RWQCB appeared to concur with the consultant's findings including the determination that the source of the impact was not related to historic or present activities at the Brandywine Distribution Center but from up-gradient sources. In the 1996 letter, the RWQCB stated that No Further Action (NFA) was required and that the RWQCB did not intend to pursue regulatory action against the current or former owners of the Brandywine Distribution Center. The case was granted regulatory closure on May 3, 2017. Based on the aforementioned, the potential exists that chlorinated hydrocarbons originating from the former Omar Rendering site and the Otay Landfill have impacted the subsurface of the subject property. The likely presence of subsurface contamination at the subject property is considered a recognized environmental condition. A controlled recognized environmental condition (CREC) refers to a REC resulting from a past release of hazardous substances or petroleum products that has been addressed to the satisfaction of the applicable regulatory authority, with hazardous substances or petroleum products allowed to remain in place subject to the implementation of required controls. The following was identified during the course of this assessment: x Partner did not identify any controlled recognized environmental conditions during the course of this assessment. A historical recognized environmental condition (HREC) refers to a past release of any hazardous substances or petroleum products that has occurred in connection with the property and has been addressed to the satisfaction of the applicable regulatory authority or meeting unrestricted use criteria Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page iii established by a regulatory authority, without subjecting the property to any required controls. The following was identified during the course of this assessment: x Partner did not identify any historical recognized environmental conditions during the course of this assessment. An environmental issue refers to environmental concerns identified by Partner, which do not qualify as RECs; however, warrant further discussion. The following was identified during the course of this assessment: x Partner did not identify any environmental issues during the course of this assessment. Conclusions, Opinions and Recommendations Partner has performed a Phase I Environmental Site Assessment in conformance with the scope and limitations of ASTM Practice E1527-13 of 517 Shinohara Lane in the City of Chula Vista, San Diego County, California (the “subject property”). Any exceptions to, or deletions from, this practice are described in Section 1.5 of this report. This assessment has revealed evidence of recognized environmental conditions and/or environmental issues in connection with the subject property. Based on the conclusions of this assessment, Partner recommends the following: x The potential for vapor intrusion, from documented contaminants in up-gradient groundwater samples, should be evaluated through a limited subsurface investigation prior to development of the subject property. Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page iv TABLE OF CONTENTS 1.0 INTRODUCTION ................................................................................................................................ 1 1.1 Purpose ................................................................................................................................................................................ 1 1.2 Scope of Work ................................................................................................................................................................... 1 1.3 Limitations .......................................................................................................................................................................... 2 1.4 User Reliance ..................................................................................................................................................................... 2 1.5 Limiting Conditions ......................................................................................................................................................... 3 2.0 SITE DESCRIPTION ............................................................................................................................ 4 2.1 Site Location and Legal Description ......................................................................................................................... 4 2.2 Current Property Use ...................................................................................................................................................... 4 2.3 Current Use of Adjacent Properties .......................................................................................................................... 4 2.4 Physical Setting Sources ................................................................................................................................................ 4 2.4.1 Topography .............................................................................................................................................................. 4 2.4.2 Hydrology ................................................................................................................................................................. 5 2.4.3 Geology/Soils .......................................................................................................................................................... 5 2.4.4 Flood Zone Information ...................................................................................................................................... 5 3.0 HISTORICAL INFORMATION ............................................................................................................ 6 3.1 Aerial Photograph Review ............................................................................................................................................ 6 3.2 Fire Insurance Maps ........................................................................................................................................................ 7 3.3 City Directories .................................................................................................................................................................. 7 3.4 Historical Topographic Maps ...................................................................................................................................... 7 4.0 REGULATORY RECORDS REVIEW .................................................................................................... 9 4.1 Regulatory Agencies ....................................................................................................................................................... 9 4.1.1 Health Department ............................................................................................................................................... 9 4.1.2 Fire Department ..................................................................................................................................................... 9 4.1.3 Air Pollution Control Agency ............................................................................................................................. 9 4.1.4 Regional Water Quality Agency .................................................................................................................... 10 4.1.5 Department of Toxic Substances Control ................................................................................................. 10 4.1.6 Building Department ......................................................................................................................................... 10 4.1.7 Planning Department ........................................................................................................................................ 11 4.1.8 Oil & Gas Exploration ........................................................................................................................................ 11 4.1.9 Assessor’s Office .................................................................................................................................................. 11 4.2 Mapped Database Records Search ........................................................................................................................ 11 4.2.1 Regulatory Database Summary ..................................................................................................................... 12 4.2.2 Subject Property Listings ................................................................................................................................. 12 4.2.3 Adjacent Property Listings .............................................................................................................................. 12 4.2.4 Sites of Concern Listings .................................................................................................................................. 14 4.2.5 Orphan Listings .................................................................................................................................................... 15 5.0 USER PROVIDED INFORMATION AND INTERVIEWS .................................................................. 16 5.1 Interviews ......................................................................................................................................................................... 17 5.1.1 Interview with Owner ........................................................................................................................................ 17 5.1.2 Interview with Report User .............................................................................................................................. 17 5.1.3 Interview with Key Site Manager .................................................................................................................. 17 Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page v 5.1.4 Interviews with Past Owners, Operators and Occupants .................................................................... 17 5.1.5 Interview with Others ........................................................................................................................................ 17 5.2 User Provided Information ........................................................................................................................................ 17 5.2.1 Title Records, Environmental Liens, and AULs ......................................................................................... 17 5.2.2 Specialized Knowledge ..................................................................................................................................... 17 5.2.3 Actual Knowledge of the User ....................................................................................................................... 18 5.2.4 Valuation Reduction for Environmental Issues ....................................................................................... 18 5.2.5 Commonly Known or Reasonably Ascertainable Information .......................................................... 18 5.2.6 Previous Reports and Other Provided Documentation ....................................................................... 18 6.0 SITE RECONNAISSANCE ................................................................................................................. 19 6.1 General Site Characteristics ....................................................................................................................................... 19 6.2 Potential Environmental Hazards............................................................................................................................ 20 6.3 Non-ASTM Services ...................................................................................................................................................... 21 6.3.1 Asbestos-Containing Materials (ACMs) ..................................................................................................... 21 6.3.2 Lead-Based Paint (LBP) ..................................................................................................................................... 21 6.3.3 Radon ...................................................................................................................................................................... 21 6.3.4 Lead in Drinking Water ..................................................................................................................................... 22 6.4 Adjacent Property Reconnaissance ........................................................................................................................ 22 7.0 FINDINGS AND CONCLUSIONS ..................................................................................................... 23 8.0 SIGNATURES OF ENVIRONMENTAL PROFESSIONALS ............................................................... 25 9.0 REFERENCES ..................................................................................................................................... 26 Figures Figure 1 Site Location Map Figure 2 Site Plan Figure 3 Topographic Map Appendices Appendix A Site Photographs Appendix B Historical/Regulatory Documentation Appendix C Regulatory Database Report Appendix D Qualifications Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page 1 1.0 INTRODUCTION Partner Engineering and Science, Inc. (Partner) has performed a Phase I Environmental Site Assessment ESA) in general conformance with the scope and limitations of ASTM Standard Practice E1527-13 and the Environmental Protection Agency Standards and Practices for All Appropriate Inquiries (AAI) (40 CFR Part 312) for the property located at 517 Shinohara Lane in the City of Chula Vista, San Diego County, California (the “subject property”). Any exceptions to, or deletions from, this scope of work are described in the report. 1.1 Purpose The purpose of this ESA is to identify existing or potential Recognized Environmental Conditions (as defined by ASTM Standard E1527-13) affecting the subject property that: 1) constitute or result in a material violation or a potential material violation of any applicable environmental law; 2) impose any material constraints on the operation of the subject property or require a material change in the use thereof; 3) require clean-up, remedial action or other response with respect to Hazardous Substances or Petroleum Products on or affecting the subject property under any applicable environmental law; 4) may affect the value of the subject property; and 5) may require specific actions to be performed with regard to such conditions and circumstances. The information contained in the ESA Report will be used by Client to: 1) evaluate its legal and financial liabilities for transactions related to foreclosure, purchase, sale, loan origination, loan workout or seller financing; 2) evaluate the subject property’s overall development potential, the associated market value and the impact of applicable laws that restrict financial and other types of assistance for the future development of the subject property; and/or 3) determine whether specific actions are required to be performed prior to the foreclosure, purchase, sale, loan origination, loan workout or seller financing of the subject property. This ESA was performed to permit the User to satisfy one of the requirements to qualify for the innocent landowner, contiguous property owner, or bona fide prospective purchaser limitations on scope of Comprehensive Environmental Response, Compensation and Liability Act (CERCLA) (42 U.S.C. §9601) liability (hereinafter, the “landowner liability protections,” or “LLPs”). ASTM Standard E1527-13 constitutes all appropriate inquiry into the previous ownership and uses of the property consistent with good commercial or customary practice” as defined at 42 U.S.C. §9601(35)(B). 1.2 Scope of Work The scope of work for this ESA is in general accordance with the requirements of ASTM Standard E1527- 13. This assessment included: 1) a property and adjacent site reconnaissance; 2) interviews with key personnel; 3) a review of historical sources; 4) a review of regulatory agency records; and 5) a review of a regulatory database report provided by a third-party vendor. Partner contacted local agencies, such as environmental health departments, fire departments and building departments in order to determine any current and/or former hazardous substances usage, storage and/or releases of hazardous substances on the subject property. Additionally, Partner researched information on the presence of activity and use limitations (AULs) at these agencies. As defined by ASTM E1527-13, AULs are the legal or physical restrictions or limitations on the use of, or access to, a site or facility: 1) to reduce or eliminate potential Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page 2 exposure to hazardous substances or petroleum products in the soil or groundwater on the subject property; or 2) to prevent activities that could interfere with the effectiveness of a response action, in order to ensure maintenance of a condition of no significant risk to public health or the environment. These legal or physical restrictions, which may include institutional and/or engineering controls (IC/ECs), are intended to prevent adverse impacts to individuals or populations that may be exposed to hazardous substances and petroleum products in the soil or groundwater on the property. If requested by Client, this report may also include the identification, discussion of, and/or limited sampling of asbestos-containing materials (ACMs), lead-based paint (LBP), mold, and/or radon. 1.3 Limitations Partner warrants that the findings and conclusions contained herein were accomplished in accordance with the methodologies set forth in the Scope of Work. These methodologies are described as representing good commercial and customary practice for conducting an ESA of a property for the purpose of identifying recognized environmental conditions. There is a possibility that even with the proper application of these methodologies there may exist on the subject property conditions that could not be identified within the scope of the assessment or which were not reasonably identifiable from the available information. Partner believes that the information obtained from the record review and the interviews concerning the subject property is reliable. However, Partner cannot and does not warrant or guarantee that the information provided by these other sources is accurate or complete. The conclusions and findings set forth in this report are strictly limited in time and scope to the date of the evaluations. The conclusions presented in the report are based solely on the services described therein, and not on scientific tasks or procedures beyond the scope of agreed-upon services or the time and budgeting restraints imposed by the Client. No other warranties are implied or expressed. Some of the information provided in this report is based upon personal interviews, and research of available documents, records, and maps held by the appropriate government and private agencies. This report is subject to the limitations of historical documentation, availability, and accuracy of pertinent records, and the personal recollections of those persons contacted. This practice does not address requirements of any state or local laws or of any federal laws other than the all appropriate inquiry provisions of the LLPs. Further, this report does not intend to address all of the safety concerns, if any, associated with the subject property. Environmental concerns, which are beyond the scope of a Phase I ESA as defined by ASTM include the following: ACMs, LBP, radon, and lead in drinking water. These issues may affect environmental risk at the subject property and may warrant discussion and/or assessment; however, are considered non-scope issues. If specifically requested by the Client, these non-scope issues are discussed in Section 6.3. 1.4 User Reliance STOS Partners engaged Partner to perform this assessment in accordance with an agreement governing the nature, scope and purpose of the work as well as other matters critical to the engagement. All reports, both verbal and written, are for the sole use and benefit of STOS Partners. Either verbally or in Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page 3 writing, third parties may come into possession of this report or all or part of the information generated as a result of this work. In the absence of a written agreement with Partner granting such rights, no third parties shall have rights of recourse or recovery whatsoever under any course of action against Partner, its officers, employees, vendors, successors or assigns. Any such unauthorized user shall be responsible to protect, indemnify and hold Partner, Client and their respective officers, employees, vendors, successors and assigns harmless from any and all claims, damages, losses, liabilities, expenses (including reasonable attorneys’ fees) and costs attributable to such Use. Unauthorized use of this report shall constitute acceptance of and commitment to these responsibilities, which shall be irrevocable and shall apply regardless of the cause of action or legal theory pled or asserted. Additional legal penalties may apply. This report has been completed under specific Terms and Conditions relating to scope, relying parties, limitations of liability, indemnification, dispute resolution, and other factors relevant to any reliance on this report. Any parties relying on this report do so having accepted the Terms and Conditions for which this report was completed. A copy of Partner’s standard Terms and Conditions can be found at http://www.partneresi.com/terms-and-conditions.php. 1.5 Limiting Conditions The findings and conclusions contain all of the limitations inherent in these methodologies that are referred to in ASTM E1527-13. Specific limitations and exceptions to this ESA are more specifically set forth below: x Interviews with past owners, operators and occupants were not reasonably ascertainable and thus constitute a data gap. Based on information obtained from other historical sources (as discussed in Section 3.0), this data gap is not expected to alter the findings of this assessment. x Partner submitted a Freedom of Information Act (FOIA) request to the Chula Vista Building Department (CVBD) for information pertaining to hazardous substances, underground storage tanks, releases, inspection records, etc. for the subject property and/or adjacent properties. As of this writing, the Chula Vista Building Department (CVBD) has not responded to Partner’s request. Based on information obtained from other historical sources, this limitation is not expected to alter the overall findings of this assessment. x Partner requested information relative to deed restrictions and environmental liens, and a title search. This information was not provided at the time of the assessment. Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page 4 2.0 SITE DESCRIPTION 2.1 Site Location and Legal Description The subject property at 517 Shinohara Lane in Chula Vista, California is located at the western terminus of Shinohara Lane, approximately 350 feet west of Brandywine Avenue. According to online research, the abbreviated legal description of the subject property is “SEC 19-18-1W*LOT 1*(EX ST)DOC91-685199 IN,” and ownership is currently vested in San Francisco Assets, LLC and Selma Investments, LLC since 2009. Please refer to Figure 1: Site Location Map, Figure 2: Site Plan, Figure 3: Topographic Map, and Appendix A: Site Photographs for the location and site characteristics of the subject property. 2.2 Current Property Use The subject property is currently undeveloped land. No operations are conducted on site. The subject property is designated for industrial development by the City of Chula Vista. The subject property was not identified in the regulatory database report of Section 4.2. 2.3 Current Use of Adjacent Properties The subject property is located within a mixed commercial/industrial/residential area of San Diego County. During the vicinity reconnaissance, Partner observed the following land use on properties in the immediate vicinity of the subject property: Immediately Surrounding Properties North: Mendocino residential condominium complex (1555-1595 Mendocino Drive) South: A multi-unit light industrial building (505 Main Street) and Fuller Collision Center (515 Main Street) East: Two multi-unit light industrial buildings (1670 and 1690 Brandywine Avenue) and Shinohara Lane West: A single-family residential community The adjacent properties to the east were identified as CA WMUDS/SWAT and CA SLIC sites in the regulatory database report of Section 4.2. 2.4 Physical Setting Sources 2.4.1 Topography The United States Geological Survey (USGS) Imperial Beach, California Quadrangle 7.5-minute series topographic map was reviewed for this ESA. According to the contour lines on the topographic map, the subject property is located at approximately 200 feet above mean sea level (MSL). The contour lines in the area of the subject property indicate the area is sloping moderately toward the south. The subject property is depicted on the 2012 map as undeveloped. A copy of the most recent topographic map is included as Figure 3 of this report. Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page 5 2.4.2 Hydrology According to topographic map interpretation, the direction of groundwater in the vicinity of the subject property is inferred to flow toward the southwest. The nearest surface water in the vicinity of the subject property is the Otay River located approximately one-quarter mile south of the subject property. No settling ponds, lagoons, surface impoundments, wetlands or natural catch basins were observed at the subject property during this assessment. According to available information, a public water system operated by the Otay Water District serves the subject property vicinity. According to the Otay Water District website, shallow groundwater beneath the subject property is not utilized for domestic purposes. The Otay Water District purchases water from the San Diego County Water Authority (CWA), a public agency that operates as a wholesale water supplier in San Diego County. Much of this water is in turn purchased from the Los Angeles-based Metropolitan Water District of Southern California (MWD), another public agency that imports water from both Northern California (through the State Water Project) and the Colorado River. According to a previous subsurface investigation conducted on the east adjacent properties (1670 and 1690 Brandywine Avenue and Case 9 000247N96), the depth of groundwater in the vicinity of the subject property is inferred to be approximately 45 to 85 feet below ground surface (bgs). 2.4.3 Geology/Soils The subject property is situated within the San Diego plain of the Coast Ranges physiographic province of the State of California The coastal plain is characterized by a series of dissected wave-cut terraces (mesas) extending inland from the coast. These terraces are underlain by generally flat-lying Cretaceous and Eocene sedimentary formations, which, in turn, are capped by relatively thin deposits of Pliocene and Pleistocene age. Directly below this latter unit is the Pliocene age San Diego Formation, which consists predominantly of sandstone. Based on information obtained from the USDA Natural Resources Conservation Service Web Soil Survey online database, the subject property is mapped as mainly Salinas clay loam with about 15 percent of the northwestern corner of the property Olivenhain cobbly loam. The Salinas series consists of deep, well-drained, moderately permeable soils that formed on alluvial plains from alluvium derived from mixed sources. Slopes range from 2 to 9 percent. The Olivenhain series consists of shallow, well-drained, very low to moderately low permeable soils that formed on marine terraces from gravelly alluvium derived from mixed sources. Slopes range from 2 to 30 percent. 2.4.4 Flood Zone Information Partner performed a review of the Flood Insurance Rate Map, published by the Federal Emergency Management Agency. According to Community Panel Numbers 2156G and 2157G, dated May 16, 2012, the subject property appears to be located in Zone X, an area located outside of the 100-year and 500- year flood plains. A copy of the reviewed flood map is not included in Appendix B of this report. Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page 6 3.0 HISTORICAL INFORMATION Partner obtained historical use information about the subject property from a variety of sources. A chronological listing of the historical data found is summarized in the table below: Historical Use Information Period/Date Source Description/Use 1904-Present Aerial Photographs, Topographic Maps, City Directories, Onsite Observations Undeveloped Land No tenants have ever occupied the subject property. Recognized environmental conditions were identified in association with the subject property, as further discussed in Section 4.2.3. 3.1 Aerial Photograph Review Partner obtained available aerial photographs of the subject property and surrounding area from Environmental Data Resources (EDR) on December 28, 2017. The following observations were noted to be visible on the subject property and adjacent properties during the aerial photograph review: Date: 1949 Scale: 1”=500’ Subject Property: Undeveloped North: Undeveloped South: Undeveloped East: Undeveloped West: Undeveloped Date: 1953, 1964 Scale: 1”=500’ Subject Property: Undeveloped North: Undeveloped South: Greenhouses East: Undeveloped West: Undeveloped Date: 1966, 1970 Scale: 1”=500’ Subject Property: Undeveloped North: Undeveloped South: Greenhouses East: Agricultural land West: The current single-family residential community Date: 1979 Scale: 1”=500’ Subject Property: Undeveloped North: The current residential condominium complex South: Vacant land East: Agricultural land West: The current single-family residential community Date: 1985 Scale: 1”=500’ Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page 7 Date: 1985 Scale: 1”=500’ Subject Property: Undeveloped North: The current residential condominium complex South: The current two commercial buildings East: Vacant land West: The current single-family residential community Date: 1989, 1994, 2005, 2009, 2010, 2012 Scale: 1”=500’ Subject Property: Undeveloped North: The current residential condominium complex South: The current two commercial buildings East: The current two commercial buildings and Shinohara Lane West: The current single-family residential community Copies of select aerial photographs are included in Appendix B of this report. 3.2 Fire Insurance Maps Partner reviewed the collection of Sanborn Fire insurance maps from Environmental Data Resources (EDR) on December 29, 2017. Sanborn map coverage was not available for the subject property. A copy of the Sanborn No Coverage Letter is included in Appendix B of this report. 3.3 City Directories Partner reviewed historical city directories obtained from Environmental Data Resources (EDR) on December 28, 2017 for past names and businesses that were listed for the subject property and adjacent properties. City directories were not identified for the subject property. Based on the city directory review, no environmentally sensitive listings were identified for the subject property address. According to the city directory review, the adjacent properties have been occupied by commercial businesses and private residential parties dating back to 1970. Neighboring properties of environmental concern, if any, are discussed in Section 4.2. Copies of reviewed city directories are included in Appendix B of this report. 3.4 Historical Topographic Maps Partner reviewed historical topographic maps obtained from Environmental Data Resources (EDR) on December 27, 2017. The following observations were noted to be depicted on the subject property and adjacent properties during the topographic map review: Date: 1904, 1930, 1943, 1953 Subject Property: Undeveloped native land North: Undeveloped native land South: Undeveloped native land East: Undeveloped native land Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page 8 Date: 1904, 1930, 1943, 1953 West: Undeveloped native land Date: 1975 Subject Property: Undeveloped native land North: Shaded to indicate urban development South: Four small structures East: Undeveloped native land West: The current single-family residential community Date: 1991 Subject Property: Undeveloped native land North: Shaded to indicate urban development South: The current two commercial buildings East: The current two commercial buildings West: Shaded to indicate urban development Date: 1996 Subject Property: Shaded to indicate urban development North: Shaded to indicate urban development South: Shaded to indicate urban development East: Shaded to indicate urban development West: Shaded to indicate urban development Date: 2012 Subject Property: Undeveloped land North: Undeveloped land South: Undeveloped land East: Undeveloped and Shinohara Lane West: Undeveloped land Copies of reviewed topographic maps are included in Appendix B of this report. Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page 9 4.0 REGULATORY RECORDS REVIEW 4.1 Regulatory Agencies 4.1.1 Health Department Regulatory Agency Data Name of Agency: San Diego County Department of Environmental Health (SDCDEH) Point of Contact: Mr. Edwin C. Andrus Agency Address: 5510 Overland Avenue, Suite 170, San Diego, California 92112 Agency Phone Number: (858) 505-6700 / (858) 505-6937 Date of Contact: December 27, 2017 Method of Communication: Email Summary of Communication: No records regarding hazardous substance use, storage or releases, or the presence of USTs and AULs on the subject property were on file with the SDCDEH. A copy of pertinent documents is not included in Appendix B of this report. 4.1.2 Fire Department Regulatory Agency Data Name of Agency: City of Chula Vista Fire Department (CVFD) Point of Contact: City Clerk’s Office Agency Address: 447 F Street, Chula Vista, California 91910 Agency Phone Number: (619) 691-5055 Date of Contact: December 27, 2017 Method of Communication: Telephone Summary of Communication: Jurisdiction over management of hazardous materials, hazardous waste, and underground storage tanks (USTs) within the City of San Diego falls under the oversight of the SDCDEH, Hazardous Materials Management Division (HMMD) and Site Assessment and Mitigation Program (SAM), and not the CVFD, as discussed in Section 4.1.2, Health Department, above. A copy of pertinent documents is not included in Appendix B of this report. 4.1.3 Air Pollution Control Agency Regulatory Agency Data Name of Agency: San Diego Air Pollution Control District (SDAPCD) Point of Contact: https://publicservices.sdcounty.ca.gov/citizenaccess/ Agency Address: 10124 Old Grove Road, San Diego, California 92131 Agency Phone Number: (858) 586-2600 Date of Contact: December 27, 2017 Method of Communication: On line Summary of Communication: No Permits to Operate (PTO), Notices of Violation (NOV), or Notices to Comply (NTC) or the presence of AULs, dry cleaning machines, or USTs were on file for the subject property with the SDAPCD. Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page 10 A copy of pertinent documents is not included in Appendix B of this report. 4.1.4 Regional Water Quality Agency Regulatory Agency Data Name of Agency: California State Water Quality Control Board (SWQCB)–San Diego Region Point of Contact: http://geotracker.waterboards.ca.gov/default.asp Agency Address: 2375 Northside Drive, Suite 100, San Diego, California 92108 Agency Phone Number: (619) 516-1990 Date of Contact: December 27, 2017 Method of Communication: On line Summary of Communication: The subject property address was not reported on the Geotracker database as a site where releases to the environment have occurred. A copy of pertinent documents is not included in Appendix B of this report. 4.1.5 Department of Toxic Substances Control Regulatory Agency Data Name of Agency: California Department of Toxic Substances Control (DTSC) Point of Contact: x http://www.dtsc.ca.gov/database/LUC/name_list.cfm x http://www.envirostor.dtsc.ca.gov/public/ x http://www.hwts.dtsc.ca.gov/report_search.cfm?id=5 Agency Address: 5796 Corporate Avenue, Cypress, California 92630 Agency Phone Number: (714) 484-5300 Date of Contact: December 27, 2017 Method of Communication: On line Summary of Communication: The subject property was not reported on the Envirostor database as a site where releases to the environment have occurred, on the LUC database as a site where land use restrictions have been imposed, or on the HWTS database as a site that disposed of hazardous waste under manifest. A copy of pertinent documents is not included in Appendix B of this report. 4.1.6 Building Department Regulatory Agency Data Name of Agency: Chula Vista Building Department (CVBD) Point of Contact: https://pip.chulavistaca.gov/CitizenAccess/chulavista.aspx Agency Address: 276 Fourth Avenue, Chula Vista, California 91910 Agency Phone Number: (619) 691-5272 Date of Contact: December 27, 2017 Method of Communication: On line and Telephone Summary of Communication: As of the date of this report, Partner has not received a response from the CVBD for inclusion in this report. A copy of pertinent documents is not included in Appendix B of this report. Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page 11 4.1.7 Planning Department Regulatory Agency Data Name of Agency: Chula Vista Planning Department (CVPD) Point of Contact: https://pip.chulavistaca.gov/CitizenAccess/chulavista.aspx Agency Address: 276 Fourth Avenue, Chula Vista, California 91910 Agency Phone Number: (619) 691-5272 Date of Contact: December 27, 2017 Method of Communication: On line Summary of Communication: According to records reviewed, the subject property is zoned ILP Limited Industrial Precise Plan) for industrial use by the County of San Diego. A copy of pertinent documents is not included in Appendix B of this report. 4.1.8 Oil & Gas Exploration Regulatory Agency Data Name of Agency: California Division of Oil, Gas and Geothermal Resources (DOGGR) Point of Contact: http://www.conservation.ca.gov/dog/Pages/WellFinder.aspx Agency Address: 5816 Corporate Avenue, Cypress, California 90630 Agency Phone Number: (714) 816-6847 Date of Contact: December 27, 2017 Method of Communication: On line Summary of Communication: According to the DOGGR website, no oil or gas wells are located on or adjacent to the subject property. A copy of pertinent documents is not included in Appendix B of this report. 4.1.9 Assessor’s Office Regulatory Agency Data Name of Agency: San Diego County Assessor Point of Contact: https://arcc-acclaim.sdcounty.ca.gov/search/SearchTypeParcel Agency Address: 1600 Pacific Highway, Suite 103, San Diego, California 92101 Agency Phone Number: (619) 235-5200 Date of Contact: December 27, 2017 Method of Communication: On line Summary of Communication: According to records reviewed, the subject property is identified by Assessor Parcel Number (APN) 644-040-01-00. A copy of pertinent documents is not included in Appendix B of this report. 4.2 Mapped Database Records Search Information from standard federal, state, county, and city environmental record sources was provided by Environmental Data Resources, Inc. (EDR). Data from governmental agency lists are updated and integrated into one database, which is updated as these data are released. The information contained in this report was compiled from publicly available sources and the locations of the sites are plotted utilizing Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page 12 a geographic information system, which geocodes the site addresses. The accuracy of the geocoded locations is approximately +/-300 feet. Using the ASTM definition of migration, Partner considers the migration of hazardous substances or petroleum products in any form onto the subject property during the evaluation of each site listed on the radius report, which includes solid, liquid, and vapor. 4.2.1 Regulatory Database Summary Radius Report Data Database Search Radius mile) Subject Property Adjacent Properties Sites of Concern Federal NPL or Delisted NPL Site 1.00 N N N Federal CERCLIS Site 0.50 N N N Federal CERCLIS-NFRAP Site 0.50 N N N Federal RCRA CORRACTS Facility 1.00 N N N Federal RCRA TSDF Facility 0.50 N N N Federal RCRA Generators Site (LQG, SQG, CESQG) 0.25 N N N Federal IC/EC Registries 0.50 N N N Federal ERNS Site Subject Property N N N State/Tribal Equivalent NPL 1.00 N N N State/Tribal Equivalent CERCLIS 1.00 N N Y State/Tribal Landfill/Solid Waste Disposal Site 0.50 N N Y State/Tribal Leaking Storage Tank Site 0.50 N N N State/Tribal Registered Storage Tank Sites UST/AST) 0.25 N N Y State/Tribal Voluntary Cleanup Sites (VCP) 0.50 N N N State/Tribal Spills 0.50 N N N Federal Brownfield Sites 0.50 N N N State Brownfield Sites 0.50 N N N EDR MGP Varies N N N EDR US Hist Auto Station Varies N N N EDR US Hist Cleaners Varies N N N State/Tribal SLIC (Spills, Leaks, Investigations, and Cleanups) Varies N Y N Other Miscellaneous Environmental Databases Varies N Y Y 4.2.2 Subject Property Listings The subject property is not identified in the regulatory database report. 4.2.3 Adjacent Property Listings The adjacent properties to the east were identified as CA SLIC and CA WMUDS/SWAT sites in the regulatory database report, as discussed below: Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page 13 x The properties identified as Brandywine Distribution Center at 1670 and 1690 Brandywine Avenue are located adjacent to the east of the subject property. These sites are identified as one closed SLIC case site on the State Water Quality Control Board (RWQCB) GeoTracker database. The lead agency is identified as the San Diego Regional Water Quality Control Board (RWQCB) Region 9 and the case number is 9000247N96. It has a cleanup status of “Completed – Case closed as of 5/3/17.” The case is listed as a Category 1 site, which is described as follows: Category 1 includes most leaking underground fuel tank (LUFT) sites and many small commercial facilities, such as dry cleaners. Category 1 sites are characterized by soil or groundwater contamination that does not pose an immediate human health threat and does not extend off-site onto neighboring properties. Off-site groundwater plumes that extend only into the public right of way are also included in this category. We expect little or no public interest at Category 1 sites. Based on records reviewed for the case, groundwater beneath the site was found to be impacted by chlorinated hydrocarbons (TCE reported at concentrations of 1 l to 720 l) and determined to have originated from the former Omar Rendering site and the Otay Landfill, facilities situated in up-gradient directions. Based on assessment activities conducted by Ogden Environmental and Energy Services and related in a May 1996 Soil and Groundwater Investigation report, “there did not appear to be a risk to human health at the subject site. Odgen concluded that "the source of groundwater contamination beneath the site appears to be from an off-site source." As per a 1997 report summarized in a 2017 Phase I Environmental Site Assessment Report by Partner for the Brandywine Distribution Center sites, "it is clearly evident that properties to the east and north of Brandywine Distribution Center, specifically the Omar Rendering Facility and the Otay Landfill, have affected the underlying groundwater table. Further, clear evidence indicates that the source of this impact is not related to historic or present activities at either 1670 or 1690 Brandywine Avenue." According to the 2017 Phase I Environmental Site Assessment Report for the Brandywine Distribution Center, the RWQCB reviewed the 1996 Soil and Groundwater Investigation report for the Brandywine Distribution Center and in a letter dated November 15, 1996, summarized that volatile organic compounds (VOC) including trichloroethene (TCE), tetrachloroethene (PCE), and methylene chloride (MEC) had been discovered at elevated concentrations in groundwater beneath the sites, but not in the unsaturated soil zone. Even though the RWQCB cited that the former Omar Rendering site (located approximately 700 feet to the east) and the former Otay Landfill (located about one-half mile to the northeast) had not been clearly identified as the sources of impacted groundwater beneath the Brandywine Distribution Center, the RWQCB appeared to concur with the consultant's findings. In the 1996 letter, the RWQCB stated that No Further Action (NFA) was required and that the RWQCB did not intend to pursue regulatory action against the current or former owners of the Brandywine Distribution Center. In the Phase I Environmental Site Assessment for the Brandywine Distribution Center, Partner identified the historical subsurface contamination case as an environmental concern and Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page 14 recommended no further investigation. The potential exists that chlorinated hydrocarbons originating from the former Omar Rendering site and the Otay Landfill have impacted the subsurface of the subject property. The likely presence of subsurface contamination at the subject property is considered a recognized environmental condition. x The properties identified as Brandywine Distribution Center at 1670 and 1690 Brandywine Avenue are also listed as a California WMUDS/SWAT site. CA Waste Management Unit Database WMUDS) is used by the State Water Resources Control Board (SWRCB) and the RWQCB for program tracking and inventory of waste management units. The database report lists the facility type as “Other-Does not fall into the category of Municipal/Domestic, Industrial, Agricultural or Solid Waste (Class I, II or III)” and the primary waste type as “hazardous/influent or solid wastes that contain toxic, corrosive, ignitable or reactive substances and must be managed according to applicable DOHS standards.” Based on the findings, vapor migration is not expected to represent a significant environmental concern at this time. 4.2.4 Sites of Concern Listings Properties to the east and northeast are identified as CA DEED, CA LDS, CA BOND EXP. PLAN, CA Cortese, CA ENF, CA NPDES, ENVIROSTOR, CA SWF/LF, CA San Diego Co. HMMD, CA HIST UST, CA EMI, and CA HWP sites in the regulatory database report, as discussed below: x The property, identified as Otay Sanitary Landfill at Otay Valley Road and Allied Waste at Otay Landfill at 1700 Maxwell Road, is located approximately 0.25-miles to the east-northeast of the subject property, and situated hydrologically up-gradient. This site is identified as an ENVIROSTOR, CA SWF/LF, CA San Diego Co. HMMD, CA HIST UST, CA EMI, and CA HWP site. Based on subsurface investigations conducted at the east adjacent Brandywine Distribution Center sites and as discussed above in Section 4.2.3, it appears that chlorinated hydrocarbons originating from the former Omar Rendering site and the Otay Landfill have impacted the groundwater at the east adjacent Brandywine Distribution Center sites, and the potential exists that chlorinated hydrocarbons originating from the former Omar Rendering site and the Otay Landfill have impacted the subsurface of the subject property. The likely presence of subsurface contamination at the subject property is considered a recognized environmental condition. x The property, identified as Former Omar Rendering Landfill at 1886 Auto Park Place, is located approximately 0.75-miles to the east of the subject property, and situated hydrologically up- gradient. This site is identified as a CA DEED, CA LDS, CA BOND EXP. PLAN, CA Cortese, CA ENF, CA NPDES site. Based on subsurface investigations conducted at the east adjacent Brandywine Distribution Center sites and as discussed above in Section 4.2.3, it appears that chlorinated hydrocarbons originating from the former Omar Rendering site and the Otay Landfill have impacted the groundwater at the east adjacent Brandywine Distribution Center sites, and the potential exists that chlorinated hydrocarbons originating from the former Omar Rendering site and the Otay Landfill have impacted the subsurface of the subject property. The likely presence of Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page 15 subsurface contamination at the subject property is considered a recognized environmental condition. Based on the findings, vapor migration is not expected to represent a significant environmental concern at this time. 4.2.5 Orphan Listings Five orphan listings are identified in the regulatory database report; however, based on their relative distance, down-gradient location, nature of the listing and/or regulatory status, these listings are not expected to represent significant environmental concerns. A copy of the regulatory database report is included in Appendix C of this report. Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page 16 5.0 USER PROVIDED INFORMATION AND INTERVIEWS In order to qualify for one of the Landowner Liability Protections (LLPs) offered by the Small Business Liability Relief and Brownfields Revitalization Act of 2001 (the Brownfields Amendments), the User must conduct the following inquiries required by 40 CFR 312.25, 312.28, 312.29, 312.30, and 312.31. The User should provide the following information to the environmental professional. Failure to provide this information could result in a determination that all appropriate inquiries is not complete. The User is asked to provide information or knowledge of the following: x Review Title and Judicial Records for Environmental Liens and AULs x Specialized Knowledge or Experience of the User x Actual Knowledge of the User x Reason for Significantly Lower Purchase Price x Commonly Known or Reasonably Ascertainable information x Degree of Obviousness x Reason for Preparation of this Phase I ESA Fulfillment of these user responsibilities is key to qualification for the identified defenses to CERCLA liability. Partner requested our Client to provide information to satisfy User Responsibilities as identified in Section 6 of the ASTM guidance. Pursuant to ASTM E1527-13, Partner requested the following site information from STOS Partners (User of this report). User Responsibilities Item Provided By User Not Provided By User Discussed Below Does Not Apply Environmental Pre-Survey Questionnaire X Title Records, Environmental Liens, and AULs X Specialized Knowledge X Actual Knowledge X Valuation Reduction for Environmental Issues X Identification of Key Site Manager Section 5.1.3 Reason for Performing Phase I ESA Section 1.1 Prior Environmental Reports X Other X Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page 17 5.1 Interviews 5.1.1 Interview with Owner The owners of the subject property since 2009, identified as San Francisco Assets, LLC and Selma Investments, LLC, were not available to be interviewed at the time of the assessment. 5.1.2 Interview with Report User Mr. Jason Richards, Partner, STOS Partners, and report user, was not aware of any pending, threatened, or past litigation relevant to hazardous substances or petroleum products in, on, or from the subject property; any pending, threatened, or past administrative proceedings relevant to hazardous substances or petroleum products in, on, or from the subject property; or any notices from a governmental entity regarding any possible violation of environmental laws or possible liability relating to hazardous substances or petroleum products. According to Mr. Richards, the subject property has never been developed and has been always been vacant land. Mr. Richards further stated that there are no USTs, ASTs, clarifiers, oil/water separators, groundwater monitoring wells, or hazardous substance use/storage/generation on the subject property to the best of his knowledge. Mr. Richards provided Partner with a Phase I Environmental Site Assessment report (for the east adjacent sites at 1670 and 1690 Brandywine Avenue) by Partner Engineering and Science, Inc., dated May 3, 2017, as further discussed in Section 4.2.3. 5.1.3 Interview with Key Site Manager A key site manager was not available to be interviewed at the time of this assessment. 5.1.4 Interviews with Past Owners, Operators and Occupants Interviews with past owners, operators and occupants were not conducted since information regarding the potential for contamination at the subject property was obtained from other sources. 5.1.5 Interview with Others As the subject property is not an abandoned property as defined in ASTM 1527-13, interview with others were not performed. 5.2 User Provided Information 5.2.1 Title Records, Environmental Liens, and AULs Partner was not provided with title records or environmental lien and AUL information for review as part of this assessment. 5.2.2 Specialized Knowledge No specialized knowledge of environmental conditions associated with the subject property was provided by the User at the time of the assessment. Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page 18 5.2.3 Actual Knowledge of the User No actual knowledge of any environmental lien or AULs encumbering the subject property or in connection with the subject property was provided by the User at the time of the assessment. 5.2.4 Valuation Reduction for Environmental Issues No knowledge of valuation reductions associated with the subject property was provided by the User at the time of the assessment. 5.2.5 Commonly Known or Reasonably Ascertainable Information The User did not provide information that is commonly known or reasonably ascertainable within the local community about the subject property at the time of the assessment. 5.2.6 Previous Reports and Other Provided Documentation Mr. Jason Richards, Partner, STOS Partners, and report user, provided Partner with a Phase I Environmental Site Assessment report (for the east adjacent sites at 1670 and 1690 Brandywine Avenue) by Partner Engineering and Science, Inc., dated May 3, 2017, as further discussed in Section 4.2.3. Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page 19 6.0 SITE RECONNAISSANCE The weather at the time of the site visit was sunny and clear. Refer to Section 1.5 for limitations encountered during the field reconnaissance and Sections 2.1 and 2.2 for subject property operations. The table below provides the site assessment details: Site Assessment Data Site Assessment Performed By: Sara A. Gengler Site Assessment Conducted On: January 2, 2018 No site visit personnel accompanied Partner during the field reconnaissance activities. No potential environmental concerns were identified during the onsite reconnaissance. 6.1 General Site Characteristics 6.1.1 Solid Waste Disposal Solid waste is not generated at the subject property, and no solid waste disposal contractor services the subject property. No evidence of illegal dumping of solid waste was observed during the Partner site reconnaissance. 6.1.2 Sewage Discharge and Disposal No sanitary discharge is generated at the subject property and no wastewater treatment facilities or septic systems are observed or reported on the subject property. 6.1.3 Surface Water Drainage Storm water is removed from the subject property via concrete stormwater channels throughout the site. The subject property does not appear to be a designated wetland area, based on information obtained from the United States Department of Agriculture; however, a comprehensive wetlands survey would be required in order to formally determine actual wetlands on the subject property. A natural storm water wash traversing northeast to southwest spans within the perimeter of the southeastern portion of the subject property. No other surface impoundments, wetlands, natural catch basins, settling ponds, or lagoons are located on the subject property. No drywells were identified on the subject property. 6.1.4 Source of Heating and Cooling There are no heating or cooling systems or domestic water at the subject property. 6.1.5 Wells and Cisterns No aboveground evidence of wells or cisterns was observed during the site reconnaissance. 6.1.6 Wastewater No domestic wastewater is generated at the subject property. Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page 20 6.1.7 Septic Systems No septic systems were observed or reported on the subject property. 6.1.8 Additional Site Observations No additional general site characteristics were observed during the site reconnaissance. 6.2 Potential Environmental Hazards 6.2.1 Hazardous Substances and Petroleum Products Used or Stored at the Site No hazardous substances or petroleum products were observed on the subject property during the site reconnaissance. 6.2.2 Aboveground & Underground Hazardous Substance or Petroleum Product Storage Tanks (ASTs/USTs) No evidence of current or former ASTs or USTs was observed during the site reconnaissance. 6.2.3 Evidence of Releases No spills, stains or other indications that a surficial release has occurred at the subject property were observed. 6.2.4 Polychlorinated Biphenyls (PCBs) No potential PCB-containing equipment (transformers, oil-filled switches, hoists, lifts, dock levelers, hydraulic elevators, etc) was observed on the subject property during Partner’s reconnaissance. 6.2.5 Strong, Pungent or Noxious Odors No strong, pungent or noxious odors were evident during the site reconnaissance. 6.2.6 Pools of Liquid No pools of liquid were observed on the subject property during the site reconnaissance. 6.2.7 Drains, Sumps and Clarifiers No drains, sumps, or clarifiers, other than those associated with storm water removal, were observed on the subject property during the site reconnaissance. 6.2.8 Pits, Ponds and Lagoons No pits, ponds or lagoons were observed on the subject property. 6.2.9 Stressed Vegetation No stressed vegetation was observed on the subject property. 6.2.10 Additional Potential Environmental Hazards No additional environmental hazards, including landfill activities or radiological hazards, were observed. Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page 21 6.3 Non-ASTM Services 6.3.1 Asbestos-Containing Materials (ACMs) Asbestos is the name given to a number of naturally occurring, fibrous silicate minerals mined for their useful properties such as thermal insulation, chemical and thermal stability, and high tensile strength. The Occupational Safety and Health Administration (OSHA) regulation 29 CFR 1926.1101 requires certain construction materials to be presumed to contain asbestos, for purposes of this regulation. All thermal system insulation (TSI), surfacing material, and asphalt/vinyl flooring that are present in a building constructed prior to 1981 and have not been appropriately tested are “presumed asbestos-containing material” (PACM). Due to the lack of buildings on the subject property, ACMs were not considered within the scope of this assessment. 6.3.2 Lead-Based Paint (LBP) Lead is a highly toxic metal that affects virtually every system of the body. LBP is defined as any paint, varnish, stain, or other applied coating that has 1 mg/cm2 (or 5,000 ug/g or 0.5% by weight) or more of lead. Congress passed the Residential Lead-Based Paint Hazard Reduction Act of 1992, also known as Title X”, to protect families from exposure to lead from paint, dust, and soil. Under Section 1017 of Title X, intact LBP on most walls and ceilings is not considered a “hazard,” although the condition of the paint should be monitored and maintained to ensure that it does not become deteriorated. Further, Section 1018 of this law directed the Housing and Urban Development (HUD) and the US EPA to require the disclosure of known information on LBP and LBP hazards before the sale or lease of most housing built before 1978. Due to the lack of buildings on the subject property, LBP was not considered within the scope of this assessment. 6.3.3 Radon Radon is a colorless, odorless, naturally occurring, radioactive, inert, gaseous element formed by radioactive decay of radium (Ra) atoms. The US EPA has prepared a map to assist National, State, and local organizations to target their resources and to implement radon-resistant building codes. The map divides the country into three Radon Zones, according to the table below: EPA Radon Zones EPA Zones Average Predicted Radon Levels Potential Zone 1 Exceed 4.0 pCi/L Highest Zone 2 Between 2.0 and 4.0 pCi/L Moderate Zone 3 Less than 2.0 pCi/L Low It is important to note that the EPA has found homes with elevated levels of radon in all three zones, and the US EPA recommends site-specific testing in order to determine radon levels at a specific location. However, the map does give a valuable indication of the propensity of radon gas accumulation in structures. Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page 22 Radon sampling was not conducted as part of this assessment. Review of the US EPA Map of Radon Zones places the subject property in Zone 3. Based upon the radon zone classification, radon is not considered to be a significant environmental concern. 6.3.4 Lead in Drinking Water According to available information, a public water system operated by the Otay Water District serves the subject property vicinity. According to the Otay Water District website, shallow groundwater beneath the subject property is not utilized for domestic purposes. The Otay Water District purchases water from the San Diego County Water Authority (CWA), a public agency that operates as a wholesale water supplier in San Diego County. Much of this water is in turn purchased from the Los Angeles-based Metropolitan Water District of Southern California (MWD), another public agency that imports water from both Northern California (through the State Water Project) and the Colorado River. According to the Otay Water District and the 2016 Annual Water Quality Report, water supplied to the subject property is in compliance with all State and Federal regulations pertaining to drinking water standards, including lead and copper. Water sampling was not conducted to verify water quality. Molds are microscopic organisms found virtually everywhere, indoors and outdoors. Mold will grow and multiply under the right conditions, needing only sufficient moisture (e.g. in the form of very high humidity, condensation, or water from a leaking pipe, etc.) and organic material (e.g., ceiling tile, drywall, paper, or natural fiber carpet padding). Due to the lack of buildings on the subject property, mold was not considered within the scope of this assessment. 6.4 Adjacent Property Reconnaissance The adjacent property reconnaissance consisted of observing the adjacent properties from the subject property premises. No items of environmental concern were identified on the adjacent properties during the site assessment, including hazardous substances, petroleum products, ASTs, USTs, evidence of releases, PCBs, strong or noxious odors, pools of liquids, sumps or clarifiers, pits or lagoons, stressed vegetation, or any other potential environmental hazards. Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page 23 7.0 FINDINGS AND CONCLUSIONS Findings A recognized environmental condition (REC) refers to the presence or likely presence of any hazardous substances or petroleum products in, on, or at a property: due to release to the environment; under conditions indicative of a release to the environment; or under conditions that pose a material threat of a future release to the environment. The following was identified during the course of this assessment: x Based on subsurface investigations conducted at the east adjacent Brandywine Distribution Center sites, it appears that chlorinated hydrocarbons (TCE reported at concentrations of 1 l to 720 l) potentially originating from the up-gradient former Omar Rendering site and the Otay Landfill have impacted the groundwater at the east adjacent Brandywine Distribution Center sites, and the potential exists that chlorinated hydrocarbons originating from the former Omar Rendering site and the Otay Landfill have impacted the subsurface of the subject property. The Regional Water Quality Control Board (RWQCB), the lead oversight agency, reviewed a 1996 Soil and Groundwater Investigation report for the Brandywine Distribution Center case and in a letter dated November 15, 1996, summarized that volatile organic compounds (VOC) including trichloroethene (TCE), tetrachloroethene (PCE), and methylene chloride (MEC) had been discovered at elevated concentrations in groundwater beneath the sites, but not in the unsaturated soil zone. Even though the RWQCB cited that the former Omar Rendering site and the former Otay Landfill had not been clearly identified as the sources of impacted groundwater beneath the Brandywine Distribution Center, the RWQCB appeared to concur with the consultant's findings including the determination that the source of the impact was not related to historic or present activities at the Brandywine Distribution Center but from up-gradient sources. In the 1996 letter, the RWQCB stated that No Further Action (NFA) was required and that the RWQCB did not intend to pursue regulatory action against the current or former owners of the Brandywine Distribution Center. The case was granted regulatory closure on May 3, 2017. Based on the aforementioned, the potential exists that chlorinated hydrocarbons originating from the former Omar Rendering site and the Otay Landfill have impacted the subsurface of the subject property. The likely presence of subsurface contamination at the subject property is considered a recognized environmental condition. A controlled recognized environmental condition (CREC) refers to a REC resulting from a past release of hazardous substances or petroleum products that has been addressed to the satisfaction of the applicable regulatory authority, with hazardous substances or petroleum products allowed to remain in place subject to the implementation of required controls. The following was identified during the course of this assessment: x Partner did not identify any controlled recognized environmental conditions during the course of this assessment. A historical recognized environmental condition (HREC) refers to a past release of any hazardous substances or petroleum products that has occurred in connection with the property and has been Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page 24 addressed to the satisfaction of the applicable regulatory authority or meeting unrestricted use criteria established by a regulatory authority, without subjecting the property to any required controls. The following was identified during the course of this assessment: x Partner did not identify any historical recognized environmental conditions during the course of this assessment. An environmental issue refers to environmental concerns identified by Partner, which do not qualify as RECs; however, warrant further discussion. The following was identified during the course of this assessment: x Partner did not identify any environmental issues during the course of this assessment. Conclusions, Opinions and Recommendations Partner has performed a Phase I Environmental Site Assessment in conformance with the scope and limitations of ASTM Practice E1527-13 of 517 Shinohara Lane in the City of Chula Vista, San Diego County, California (the “subject property”). Any exceptions to, or deletions from, this practice are described in Section 1.5 of this report. This assessment has revealed evidence of recognized environmental conditions and/or environmental issues in connection with the subject property. Based on the conclusions of this assessment, Partner recommends the following: x The potential for vapor intrusion, from documented contaminants in up-gradient groundwater samples, should be evaluated through a limited subsurface investigation prior to development of the subject property. Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page 25 8.0 SIGNATURES OF ENVIRONMENTAL PROFESSIONALS Partner has performed a Phase I Environmental Site Assessment of the property located at 517 Shinohara Lane in the City of Chula Vista, San Diego County, California in general conformance with the scope and limitations of the protocol and the limitations stated earlier in this report. Exceptions to or deletions from this protocol are discussed earlier in this report. By signing below, Partner declares that, to the best of our professional knowledge and belief, we meet the definition of Environmental Professional as defined in §312.10 of 40 CFR §312. Partner has the specific qualifications based on education, training, and experience to assess a property of the nature, history, and setting of the subject property. Partner has developed and performed the all appropriate inquiries in conformance with the standards and practices set forth in 40 CFR Part 312. Prepared By: DRAFT Sara A. Gengler Environmental Professional Reviewed By: DRAFT Thomas Petersen, REPA Senior Project Manager Phase I Environmental Site Assessment Project No. 17-199602.1 January 16, 2018 Page 26 9.0 REFERENCES Reference Documents American Society for Testing and Materials, Standard Practice for Environmental Site Assessments: Phase I Environmental Site Assessment Process, ASTM Designation: E1527-13. Environmental Data Resources (EDR), Radius Report, January 2018 Federal Emergency Management Agency, Federal Insurance Administration, National Flood Insurance Program, Flood Insurance Map, accessed via internet, January 2018 United States Department of Agriculture, Natural Resources Conservation Service, accessed via internet, January 2018 United States Department of Agriculture, Natural Resources Conservation Service, Web Soil Survey, accessed via the internet, January 2018 United States Environmental Protection Agency, EPA Map of Radon Zones (Document EPA-402-R-93-071), accessed via the internet, January 2018 United States Geological Survey, accessed via the Internet, January 2018 United States Geological Survey Topographic Map 1995, 7.5 minute series, accessed via internet, January 2018 FIGURES 1 SITE LOCATION MAP 2 SITE PLAN 3 TOPOGRAPHIC MAP FIGURE 1: SITE LOCATION MAP Project No. 17-199602.1 Drawing Not To Scale FIGURE 2: SITE PLAN Project No. 17-199602.1 Mendocino Residential Condominium Complex (1555-1595 Mendocino Drive) GROUNDWATER FLOW Subject Property KEY: Shinohara Lane Multi-Unit Light Industrial Building 1670 Brandywine Avenue) Multi-Unit Light Industrial Building 505 Main Street) Single-Family Residences Fuller Collision Center 515 Main Street) Multi-Unit Light Industrial Building 1690 Brandywine Avenue) FIGURE 3: TOPOGRAPHIC MAP Project No. 17-199602.1 USGS 7.5 Minute Imperial Beach, CA Quadrangle Created: 2012 APPENDIX A: SITE PHOTOGRAPHS APPENDIX A: SITE PHOTOGRAPHS Project No. 17-199602.1 1. The southeastern entrance to the subject property beyond Shinohara Lane. 2. The southeastern portion of concrete stormwater channels throughout the subject property. 3. The southeastern portion of the subject property. 4. The southernmost portion of the subject property. 5. The southwestern portion of the subject property with west-adjacent single-family homes beyond. 6. The east-central portion of the subject property. APPENDIX A: SITE PHOTOGRAPHS Project No. 17-199602.1 7. The north-central portion of the subject property with the north-adjacent condominium complex beyond. 8. The west-central portion of the subject property with west-adjacent single-family homes beyond. 9. The southeastern portion of the subject property with east-adjacent commercial buildings beyond. 10. Stormwater channel on the central portion of the subject property with the east-adjacent building beyond. 11. The southwestern portion of the subject property with one of two south-adjacent buildings beyond. 12. The north-central portion of the subject property. APPENDIX A: SITE PHOTOGRAPHS Project No. 17-199602.1 13. The north-central portion of the subject property. 14. The northeasternmost portion of the subject property with the east-adjacent commercial building beyond. 15. East-adjacent Shinohara Lane. 16. The southeast- and south-adjacent properties beyond the southeastern portion of the subject property. 17. West-adjacent single-family homes beyond the northwestern portion of the subject property. 18. North-adjacent residential condominium complex beyond the northern portion of the subject property. APPENDIX A: SITE PHOTOGRAPHS Project No. 17-199602.1 19. North-adjacent residential condominium complex. 20. East-adjacent property beyond the central portion of subject property. 21. The southeast-adjacent property and the south- adjacent property vehicle storage yard. 22. One of two south-adjacent properties. 23. The two south-adjacent properties. 24. West-adjacent single family homes beyond the southwestern portion of the subject property. APPENDIX B: HISTORICAL/REGULATORY DOCUMENTATION The EDR Aerial Photo Decade Package Industrial Land 517 Shinohara Lane Chula Vista, CA 91911 Inquiry Number: December 28, 2017 5146125.9 6 Armstrong Road, 4th floor Shelton, CT 06484 Toll Free: 800.352.0050 www.edrnet.com 1949 1"=500'Flight Date: February 16, 1949 USDA 1953 1"=500'Flight Date: April 14, 1953 USDA 1964 1"=500'Flight Date: April 07, 1964 USDA 1966 1"=500'Flight Date: November 02, 1966 USGS 1970 1"=500'Flight Date: March 06, 1970 EDR Proprietary Landiscor 1979 1"=500'Flight Date: January 27, 1979 EDR Proprietary Landiscor 1985 1"=500'Flight Date: August 05, 1985 USDA 1989 1"=500'Flight Date: August 14, 1989 USDA 1994 1"=500'Acquisition Date: May 31, 1994 USGS/DOQQ 2005 1"=500'Flight Year: 2005 USDA/NAIP 2009 1"=500'Flight Year: 2009 USDA/NAIP 2010 1"=500'Flight Year: 2010 USDA/NAIP 2012 1"=500'Flight Year: 2012 USDA/NAIP EDR Aerial Photo Decade Package 12/28/17 Industrial Land Site Name:Client Name: Partner Engineering and Science, Inc. 517 Shinohara Lane 2154 Torrance Blvd, Suite 200 Chula Vista, CA 91911 Torrance, CA 90501-0000 EDR Inquiry #5146125.9 Contact:Adrian Rivas Environmental Data Resources, Inc. (EDR) Aerial Photo Decade Package is a screening tool designed to assist environmental professionals in evaluating potential liability on a target property resulting from past activities. EDR’s professional researchers provide digitally reproduced historical aerial photographs, and when available, provide one photo per decade. Search Results: Year Scale Details Source When delivered electronically by EDR, the aerial photo images included with this report are for ONE TIME USE ONLY. Further reproduction of these aerial photo images is prohibited without permission from EDR. For more information contact your EDR Account Executive. Disclaimer - Copyright and Trademark Notice This Report contains certain information obtained from a variety of public and other sources reasonably available to Environmental Data Resources, Inc. It cannot be concluded from this Report that coverage information for the target and surrounding properties does not exist from other sources. NO WARRANTY EXPRESSED OR IMPLIED, IS MADE WHATSOEVER IN CONNECTION WITH THIS REPORT. ENVIRONMENTAL DATA RESOURCES, INC. SPECIFICALLY DISCLAIMS THE MAKING OF ANY SUCH WARRANTIES, INCLUDING WITHOUT LIMITATION, MERCHANTABILITY OR FITNESS FOR A PARTICULAR USE OR PURPOSE. ALL RISK IS ASSUMED BY THE USER. IN NO EVENT SHALL ENVIRONMENTAL DATA RESOURCES, INC. BE LIABLE TO ANYONE, WHETHER ARISING OUT OF ERRORS OR OMISSIONS, NEGLIGENCE, ACCIDENT OR ANY OTHER CAUSE, FOR ANY LOSS OF DAMAGE, INCLUDING, WITHOUT LIMITATION, SPECIAL, INCIDENTAL, CONSEQUENTIAL, OR EXEMPLARY DAMAGES. ANY LIABILITY ON THE PART OF ENVIRONMENTAL DATA RESOURCES, INC. IS STRICTLY LIMITED TO A REFUND OF THE AMOUNT PAID FOR THIS REPORT. Purchaser accepts this Report "AS IS". Any analyses, estimates, ratings, environmental risk levels or risk codes provided in this Report are provided for illustrative purposes only, and are not intended to provide, nor should they be interpreted as providing any facts regarding, or prediction or forecast of, any environmental risk for any property. Only a Phase I Environmental Site Assessment performed by an environmental professional can provide information regarding the environmental risk for any property. Additionally, the information provided in this Report is not to be construed as legal advice. Copyright 2017 by Environmental Data Resources, Inc. All rights reserved. Reproduction in any media or format, in whole or in part, of any report or map of Environmental Data Resources, Inc., or its affiliates, is prohibited without prior written permission. EDR and its logos (including Sanborn and Sanborn Map) are trademarks of Environmental Data Resources, Inc. or its affiliates. All other trademarks used herein are the property of their respective owners. 5146125 9-page 2 page- APPENDIX B: AERIAL PHOTOGRAPHS Project No. Key: Subject Property Aerial Photograph Year: 1949 500 1000 2000 5146125 9 2 page- APPENDIX B: AERIAL PHOTOGRAPHS Project No. Key: Subject Property Aerial Photograph Year: 1953 500 1000 2000 5146125 9 3 page- APPENDIX B: AERIAL PHOTOGRAPHS Project No. Key: Subject Property Aerial Photograph Year: 1964 500 1000 2000 5146125 9 4 page- APPENDIX B: AERIAL PHOTOGRAPHS Project No. Key: Subject Property Aerial Photograph Year: 1966 500 1000 2000 5146125 9 5 page- APPENDIX B: AERIAL PHOTOGRAPHS Project No. Key: Subject Property Aerial Photograph Year: 1970 500 1000 2000 5146125 9 6 page- APPENDIX B: AERIAL PHOTOGRAPHS Project No. Key: Subject Property Aerial Photograph Year: 1979 500 1000 2000 5146125 9 7 page- APPENDIX B: AERIAL PHOTOGRAPHS Project No. Key: Subject Property Aerial Photograph Year: 1985 500 1000 2000 5146125 9 8 page- APPENDIX B: AERIAL PHOTOGRAPHS Project No. Key: Subject Property Aerial Photograph Year: 1989 500 1000 2000 5146125 9 9 page- APPENDIX B: AERIAL PHOTOGRAPHS Project No. Key: Subject Property Aerial Photograph Year: 1994 500 1000 2000 5146125 9 10 page- APPENDIX B: AERIAL PHOTOGRAPHS Project No. Key: Subject Property Aerial Photograph Year: 2005 500 1000 2000 5146125 9 11 page- APPENDIX B: AERIAL PHOTOGRAPHS Project No. Key: Subject Property Aerial Photograph Year: 2009 500 1000 2000 5146125 9 12 page- APPENDIX B: AERIAL PHOTOGRAPHS Project No. Key: Subject Property Aerial Photograph Year: 2010 500 1000 2000 5146125 9 13 page- APPENDIX B: AERIAL PHOTOGRAPHS Project No. Key: Subject Property Aerial Photograph Year: 2012 500 1000 2000 5146125 9 14 EDR Historical Topo Map Report Inquiry Number: 6 Armstrong Road, 4th floor Shelton, CT 06484 Toll Free: 800.352.0050 www.edrnet.com with QuadMatch™ Industrial Land 517 Shinohara Lane Chula Vista, CA 91911 December 27, 2017 5146125.4 EDR Historical Topo Map Report EDR Inquiry # Search Results: P.O.# Project: Maps Provided: Disclaimer - Copyright and Trademark Notice EDR and its logos (including Sanborn and Sanborn Map) are trademarks of Environmental Data Resources, Inc. or its affiliates. All other trademarks used herein are the property of their respective owners. page- Coordinates: Latitude: Longitude: UTM Zone: UTM X Meters: UTM Y Meters: Elevation: Contact: Site Name: Client Name: 1904 1930 1943 1953 1975 1991 1996 2012 12/27/17 Industrial Land Partner Engineering and Science, Inc. 517 Shinohara Lane 2154 Torrance Blvd, Suite 200 Chula Vista, CA 91911 Torrance, CA 90501-0000 5146125.4 Adrian Rivas EDR Topographic Map Library has been searched by EDR and maps covering the target property location as provided by Partner Engineering and Science, Inc. were identified for the years listed below. EDR’s Historical Topo Map Report is designed to assist professionals in evaluating potential liability on a target property resulting from past activities. EDRs Historical Topo Map Report includes a search of a collection of public and private color historical topographic maps, dating back to the late 1800s. NA 32.597385 32° 35' 51" North 17-199602.1 -117.031519 -117° 1' 53" West Zone 11 North 497042.33 3606654.88 202.92' above sea level This Report contains certain information obtained from a variety of public and other sources reasonably available to Environmental Data Resources, Inc. It cannot be concluded from this Report that coverage information for the target and surrounding properties does not exist from other sources. NO WARRANTY EXPRESSED OR IMPLIED, IS MADE WHATSOEVER IN CONNECTION WITH THIS REPORT. ENVIRONMENTAL DATA RESOURCES, INC. SPECIFICALLY DISCLAIMS THE MAKING OF ANY SUCH WARRANTIES, INCLUDING WITHOUT LIMITATION, MERCHANTABILITY OR FITNESS FOR A PARTICULAR USE OR PURPOSE. ALL RISK IS ASSUMED BY THE USER. IN NO EVENT SHALL ENVIRONMENTAL DATA RESOURCES, INC. BE LIABLE TO ANYONE, WHETHER ARISING OUT OF ERRORS OR OMISSIONS, NEGLIGENCE, ACCIDENT OR ANY OTHER CAUSE, FOR ANY LOSS OF DAMAGE, INCLUDING, WITHOUT LIMITATION, SPECIAL, INCIDENTAL, CONSEQUENTIAL, OR EXEMPLARY DAMAGES. ANY LIABILITY ON THE PART OF ENVIRONMENTAL DATA RESOURCES, INC. IS STRICTLY LIMITED TO A REFUND OF THE AMOUNT PAID FOR THIS REPORT. Purchaser accepts this Report "AS IS". Any analyses, estimates, ratings, environmental risk levels or risk codes provided in this Report are provided for illustrative purposes only, and are not intended to provide, nor should they be interpreted as providing any facts regarding, or prediction or forecast of, any environmental risk for any property. Only a Phase I Environmental Site Assessment performed by an environmental professional can provide information regarding the environmental risk for any property. Additionally, the information provided in this Report is not to be construed as legal advice. Copyright 2017 by Environmental Data Resources, Inc. All rights reserved. Reproduction in any media or format, in whole or in part, of any report or map of Environmental Data Resources, Inc., or its affiliates, is prohibited without prior written permission. 5146125 4 2 page Topo Sheet Key This EDR Topo Map Report is based upon the following USGS topographic map sheets. 1904 Source Sheets 1904 San Diego 15-minute, 62500 1930 Source Sheets 1930 San Diego 15-minute, 62500 1943 Source Sheets 1943 San Ysidro 7.5-minute, 31680 1953 Source Sheets 1953 San Ysidro 7.5-minute, 24000 Aerial Photo Revised 1950 5146125 4 3 page Topo Sheet Key This EDR Topo Map Report is based upon the following USGS topographic map sheets. 1975 Source Sheets 1975 Imperial Beach 7.5-minute, 24000 Aerial Photo Revised 1975 1991 Source Sheets 1991 SAN DIEGO 15-minute, 50000 1996 Source Sheets 1996 Imperial Beach 7.5-minute, 24000 Aerial Photo Revised 1996 2012 Source Sheets 2012 Imperial Beach 7.5-minute, 24000 5146125 4 4 APPENDIX B: Topographic Maps Project No. Key: Subject Property Topographic Map Year: 1904 TP, San Diego, 1904, 15-minute 0 Miles 0.25 0.5 1 1.5 5146125 4 APPENDIX B: Topographic Maps Project No. Key: Subject Property Topographic Map Year: 1930 TP, San Diego, 1930, 15-minute 0 Miles 0.25 0.5 1 1.5 5146125 4 APPENDIX B: Topographic Maps Project No. Key: Subject Property Topographic Map Year: 1943 TP, San Ysidro, 1943, 7.5-minute 0 Miles 0.25 0.5 1 1.5 5146125 4 APPENDIX B: Topographic Maps Project No. Key: Subject Property Topographic Map Year: 1953 TP, San Ysidro, 1953, 7.5-minute 0 Miles 0.25 0.5 1 1.5 5146125 4 APPENDIX B: Topographic Maps Project No. Key: Subject Property Topographic Map Year: 1975 TP, Imperial Beach, 1975, 7.5-minute 0 Miles 0.25 0.5 1 1.5 5146125 4 APPENDIX B: Topographic Maps Project No. Key: Subject Property Topographic Map Year: 1991 TP, SAN DIEGO, 1991, 15-minute 0 Miles 0.25 0.5 1 1.5 5146125 4 APPENDIX B: Topographic Maps Project No. Key: Subject Property Topographic Map Year: 1996 TP, Imperial Beach, 1996, 7.5-minute 0 Miles 0.25 0.5 1 1.5 5146125 4 APPENDIX B: Topographic Maps Project No. Key: Subject Property Topographic Map Year: 2012 TP, Imperial Beach, 2012, 7.5-minute 0 Miles 0.25 0.5 1 1.5 5146125 4 I I TABLE OF CONTENTS (Continued) I SECTION TITLE PAGE 8 LIMITAnONS 8-1 I I LIST OF FIGURES I NUMBER TITLE PAGE 1-1 Project Location Map 1-2 2-1 Soil Boring Locations for Present and Previous Investigation .2-2 I 4-1 Water-table Gradient Map (2127/96)and Heat-pulse Flow Logging Results 4-3 I 4-2 Ground-water Elevations in the Project Vicinity 4-5 4-3 Soil Sampling Analytical Results 4-6 4-4 Ground-water Sampling Analytical Results 4-10 I I LIST OF TABLES I NUMBER TITLE PAGE 2-1 Analytical Results from Previous Phase II Subsurface Investigation 2-3 I 4-1 Total Organic Carbon (TOC)Results for Soil 4-7 4-2 General Minerals Results for Ground Water 4-9 4-3 Comparison of TCE and Methylene Chloride Ground-water Results I with Adjacent Sites 4-11 4-4 Metals Results for Ground Water 4-12 I 4-5 Comparison of Site Ground-water Metal Concentrations with Ground-water Data from the Omar and Otay LandfIll Sites 4-13 4-6 Summary of Heat-pulse Flow Logging Results 4-15 I 4-7 Summary of Estimated Kd Values 4-19 4-8 Estimated R Values and TCE Plume Velocities 4-19 I I I I 570920144 i i I I I I I I I I I I I I I I I I I I I LETTER A B e 570920144 TABLE OF CONTENTS (Continued) LIST OF APPENDICES TITLE Description of uses and BoringIMonitoring Well Logs ULS Report (Utility Detection Survey) Well Development and Ground-water Sampling Logs Analytical Laboratory Reports Use of a Geo Flowmeter for the Determination of Ground Water Flow Direction iii EXECUTIVE SUMMARY This limited soil and ground-water investigation,conducted between February 5 and March 13,1996,included completion and sampling of five soil borings,installation and sampling of five ground-water monitoring wells,analytical testing of soil and ground-water samples,heat pulse flow logging to determine ground water flow direction,gradient and velocity,geochemical evaluation of ground water,and report preparation. This report presents the results of a limited ground-water and soil investigation conducted by Ogden Environmental arid Energy Services Co.,Inc.(Ogden)at the Brandywine Distribution Center,located at 1670 and 1690 Brandywine Avenue in Chula Vista, California.The investigation was conducted on behalf of Chula Vista Industrial Realty, Inc.The purpose of the investigation was to verify the presence of ground-water contamination beneath the site,evaluate ground-water flow direction,velocity and gradient, and assess potential sources of identified contamination. Two previous investigations have been conducted at the site:a Phase I Environmental Site Assessment conducted by BEM Systems,Inc.in March 1994,and a Phase II subsurface environmental investigation conducted by Ceres Environmental in May 1995.Results of the Phase I site assessment indicated that no regulated or hazardous substances were found to be in current use at the site,nor were such substances being disposed of at the site. Previous tenants were primarily product distributors who would not likely use hazardous substances.The Phase II investigation results indicated that halogenated and non-:-halogenated volatile organic compounds (HVOCs and VOCs)occur in site soil and ground water.The observed soil impacts were located adjacent to the water table and likely associated with ground water contamination.According to the previous Phase I and Phase II investigation results,hazardous substances,especially compounds such as trichloroethene (TCE),tetrachloroethene (PCE),and methylene chloride that were detected in site soil and ground water were not used or likely disposed of at the site.BEM Systems therefore concluded that an offsite source of the observed VOC and HVOC contamination was likely.Known potential offsite sources include the former Omar rendering facility, located approximately 700 feet east of the site (the Omar facility accepted Class 1 liquid industrial wastes from 1959 to 1978),and the Otay Landfill,located approximately one-half mile northeast of the site.Extensive documentation exists in San Diego Regional Water Quality Control Board (SDRWQCB)files that indicates significant TCE and methylene chloride contamination occurs in soil and ground water at the Omar facility. ES-l570920144 I I I I I I I I I I I I I I I I I I I Results of this investigation indicated no detectable soil contamination (VOCs and HVOCs) occurs within the unsaturated zone onsite.However,relatively high VOC and HVOC ground-water contamination was encountered in the central portion of the site,with lower concentrations detected throughout the remainder of the site. Heat pulse flow logging results from the central portion of the site (MW-03 and MW-04) indicate that ground-water flow in this area of the site appears to be in a generally westward direction.Observed ground-water flow rates ranged from 2.7 to 13.9 feet per day.These measurements are generally consistent with the overall direction of the measured hydraulic gradient.Heat pulse flow logging of outlying wells indicated no measurable flow (MW-01 and MW-05)or variable flow (MW-02). Results of geochemical analysis of site ground water indicate that site ground water is of poor quality,with generally high total dissolved solids,hardness,electrical conductivity sulfate,and chloride.The ground water is not considered to be a potable water resource by the SDRWQCB (SDRWQCB 1995).One well (MW-02)had considerably lower general minerals results than the others,suggesting a localized freshwater source such as irrigation water or a leaking water line. Contaminant mobility calculations indicate that a TCE plume originating at the Omar facility could migrate to the subject site within a relatively short time period (0.4 to 2.7 years). Because no evidence indicates that an onsite source of the observed ground-water contamination exists,and based on the results of the ground-water flow direction,velocity and gradient measurements,the most likely source of ground water contamination appears to be the adjacent Omar facility.To be effective,potential ground-water remediation activities would have to be initiated at the offsite contaminant source rather than at the subject site. ES·2570920144 I I I I I I I I I I I I I I I I I I I 1.1 INTRODUCTION 1.2 SITE DESCRIPTION SECTION 1 INTRODUCTION AND SITE DESCRIPTION This report includes an introduction and site description (Section 1);a discussion of previous investigations conducted at the subject site (Section 2);field investigation activities Section 3);investigation results and discussion (Section 4);conclusions and recommendations (Section 5);references (Section 6)and limitations (Section 7). I-I570920144 The subject site is located along the west side of Brandywine Avenue,immediately north of Otay Valley Road,in Chula Vista,California (Figure 1-1).According to a previous Phase I Environmental Site Assessment performed for the property,the site consists of two rectangular parcels with a combined area of 9.84 acres (BEM 1994).The subject property contains two commercialnight industrial buildings located at 1670 and 1690 Brandywine Avenue,located across Shinohara Lane from each other.The majority of the site is paved with asphalt,with landscaping around the edges of the site.The site generally slopes from north to south and ranges in elevation from approximately 175 feet above mean sea level (MSL)along the northern boundary to approximately 130 feet MSL along the southern site boundary. This report presents results of a limited soil and ground-water investigation conducted at the Brandywine Distribution Center (subject site),located at 1670 and 1690 Brandywine Avenue in Chula Vista,California.A project location map is shown in Figure 1-1.This investigation was conducted by Ogden Environmental and Energy Services Company, Inc.,(Ogden)for Chula Vista Industrial Realty,Inc.at the request of Mr.Robert C. Lascelles.The investigation was conducted to verify the presence of ground-water contamination beneath the subject site,evaluate ground-water flow direction,velocity,and gradient,and assess potential sources of the identified contamination. I I I I I I I I I I I I I I I I I I I SECTION 2 PREVIOUS INVESTIGATIONS Two previous environmental investigations have been conducted at the subject site, including a Phase-I Environmental Site Assessment and a Phase II subsurface soil assessment.BEM Systems,Inc.(BEM)conducted a Phase I investigation in March, 1994.The purpose of the Phase I investigation was to identify existing or potential environmental hazards and to recommend whether further investigation would be warranted. CERES concluded that the most likely source of the observed HVOCs and VOCs in soil . and ground water was the former Omar Rendering (Omar)site,located approximately 700 feet east.of the subject site.The.Omar site is described in the 1994 BEM Phase I report as being listed in the CORTESE,CERCLIS,CALSITES,and SWIS environmental databases.According to files reviewed by CERES at the San Diego Regional Water Quality Control Board (SDRWQCB),the Omar Rendering facility accepted Class·1 liquid industrial wastes from 1959 to 1978.These liquids,which included organic solvents, According to the Phase I report,the site was believed to be previously undeveloped.Based on a site reconnaissance and interviews with current building tenants,no regulated or hazardous substances were found to be in current use at the site,nor were such substances being disposed of at the site.According to the property manager,previous tenants were primarily product distributors who would not likely use hazardous substances.Current tenants were reported to be involved in the sale or distribution of lumber,hardware,dried flowers,halogen lamps,and Easter baskets,and would not be likely to use hazardous substances (BEM 1994). 2-1 A Phase II subsurface environmental investigation conducted by Ceres Environmental CERES)in May,1995,provided data indicating that soil and ground water beneath the subject site contains halogenated and non-halogenated volatile organic compounds (HVOCs and VOCs).Four soil borings were excavated on May 12 and 15,1995,as shown in Figure 2-1.Soil samples collected at the soil/ground-water interface from borings B-1, B-3,and B-4 were submitted to an analytical laboratory .for analysis (refusal on large cobbles was encountered in B-2 prior to reaching ground water).Ground-water samples were also obtained from soil borings B-1,B-3,and B-4.Table 2-1 presents the analytical results for soil and ground water. 570920144 I I I I I I I 1 I I I I I I I I I I I B5-OSS w:::> zw wz WAREHOUSE ~ BUILDING 0 1670 Brandywine z< Ave.a: lD B-4EB B5-o4 S - B5-o3 S . SHINOHARA LANE B-3EB WAREHOUSE BUILDING 1690 Brandywine Ave. B5-o1 S B5-o2 S EBB-2 B-1 EB 0 vN.r 200OTAYVALLEYROADiI FEET LEGEND S SOIL BORING LOCATION, THIS INVESTIGATION FORMER SOIL BORING LOCATION EB FROM PREVIOUS PHASE" BASEMAP:San Diego Land Surveying &Engineering,Inc. INVESTIGATION (CERES,1995) 2-1 FIGURE Soil Boring Locations for Present and Previous Investigation••••• I I I I I I I I I I I I I I I I I I OGDEN I X:\GRAPHICSIBRANDYWIN\BASEMAP.FH5 Table 2-1 ANALYTICAL RESULTS FROM PREVIOUS PHASE II SUBSURFACE INVESTIGATION B-01-50 B-04-70 B-01-W-Ol B-03-W..fJl.B...()4..W-03 Analyte (soil)(soil)(ground water)(ground water)(ground water) Trichloroethene (TCE)<5 Ilgll 59 Ilg/kg 470 Ilgll 680 Ilgll 430 Ilgll Tetrachloroethene (PCE)<5 Ilgll <5 Ilgll 12 Ilgll 14 Ilgll 11 Ilgll l,l-dichloroethene <5 Ilgll <5 Ilgll 32 Ilgll 46 Ilgll 8.2 Ilgll l,l-dichloroethane (DCA)<5 Ilgll 5 Ilg/kg 25 Ilgll <5 Ilgll 27 Ilgll l,l,2-trichloroethane <5 Ilgll <5 Ilgll 19 Ilgll 17 Ilgll <5 Ilgll l,2-dichloroethane <5 Ilgll <5 Ilgll 41lgll 61lgll <5 Ilgll cis-l,2-dichloroethene <5 Ilgll <5 Ilgll <5 Ilgll 31lgll <5 Ilgll Methylene chloride <20 Ilgll <20 Ilgll <5 Ilgll <20 Ilgll 10 Ilgll Chlorofonn <5 Ilgll <5 Ilgll 7.9 Ilgll 11 Ilgll 4.3 Ilgll Benzene <5 Ilgll <5 Ilgll <5 Ilgll 3.1 Ilgll <5 Ilgll Total xylenes 6.2 Ilg/kg <5 Ilgll <5 Ilgll <5 Ilgll <5 Ilgll Source:CERES 1995 Ilglkg micrograms per kilogram Ilg /l micrograms per liter 5 Indicates laboratory detection limit B-Ol-50 Boring (B)-Boring Number (01)-Depth Below Ground Surface (50 feet) B-03-W..fJl.Boring (B)-Boring Number (03)-Water Sample (W)-Sample Number (02) I I I I I I I I I I I I I I I I I I I 570920144 2-3 were stored in large surface impoundments in the northern portion of the site (CERES 1995). Based on the proximity of the Omar site to the subject property,the period of time that evaporation ponds _were in operation,and the anticipated southwestward ground-water flow direction,CERES concluded that the adjacent Omar site was most likely the source of ground-water contamination beneath the subject site.The Otay Landfill,located approximately 1/2 mile northeast of the subject property,was also identified as a possible secondary contamination source (CERES 1995). Available SNM files were also reviewed for the property occupied by Hyspan Precision Products,Inc.This property is located at 1685 Brandywine Avenue,directly east of the subject site on the eastern side of Brandywine Avenue.According to the County of San Diego Compliance Inspection Report,a single I,OOO-gallon diesel fuel underground storage tank (UST)was removed from the property in February,1986.No indication of soil or ground-water contamination was apparent in the tank excavation.In addition,a 1994 Compliance Inspection Report for the Hyspan property indicates that onsite machinery was observed to be leaking oil to the ground.Available records did not indicate that any other hazardous materials releases,leaks,or removals have been reported at this property.Based on these records,the Hyspan property does not appear to be a possible source for HVOCs and VOCs detected in ground water at the subject site. Files reviewed by Ogden at the Site Assessment and Mitigation (SNM)Division of the County of San Diego Department of Environmental Health indicate that ground-water contamination beneath the Omar site is well documented.A site investigation report for the Omar site by Dames and Moore (1989)indicates that trichloroethene (TCE)was detected in 7 of 9 ground-water monitoring wells at concentrations ranging from 3 to 1,100 parts per billion (ppb).In addition,several metals were detected in ground-water samples,with mercury and selenium exceeding primary drinking water standards in several monitoring wells.An annual ground-water monitoring report by Dames and Moore (1995)indicates that TCE concentrations as high as 3,000 micrograms per liter (Jlg/l)were measured in ground water beneath the Omar site between 1989 and 1994.A 1996 addendum to the 1989 Dames and Moore report by Risk-Based Decisions,Inc.indicates that a ground-water TCE concentration of 21,000 Jlg/l was measured in a monitoring well located within the area occupied by the former southwestern surface impoundment at the Omar site. 2-4570920144 I I I I I I I I I I I I I I I I I I I 3.2 SOIL SAMPLING 3.1 UNDERGROUND UTILITY CHECK AND UTILITY DETECTION SURVEY SECTION 3 FIELD INVESTIGATION ACTIVITIES Soil borings were conducted using a Failing F-6 drill rig equipped with 8-inch (outside diameter)hollow-stem augers.Soil cuttings were examined every 10 feet to identify 3-1570920144 The current field investigation activities were performed by Ogden at the subject property between February-5 and March 13,1996.The activities included a subsurface utility detection survey;drilling and soil sampling;installation,development,and sampling of monitoring wells;land surveying;heat-pulse flow logging;and management of investigation-derived waste (lOW).The following sections describe these activities. Underground Service Alert (USA)was contacted prior to commencement of field activities. All utility companies contacted by USA indicated that no underground utilities were present in the direct vicinity (i.e.,within 5 feet)of proposed boring/monitoring well locations. An underground utility detection survey was conducted by Underground Location Services Company (ULS)of La Jolla,California,on February 5,1996.The underground utility survey was conducted to locate and identify underground cables,pipes and utilities at each boring location.ULS performed an Electromagnetic Pipe and Cable Location (EMPCL) conductive utility survey,which utilized passive,ground induction and connection modes. ULS also conducted an Electromagnetic Induction (EMIND)sweep for potential metal mass interference.A lO-foot radius around each boring was investigated.No anomalous readings or underground utilities were identified at any of the five boring locations surveyed.The utility detection survey report by ULS is included in Appendix A. Soil sampling activities were conducted on February 10 and 11,and on February 17 and 18,1996.Valley Well Drilling of Ventura,California,provided the drilling services.A total of five soil borings were conducted to depths ranging from 56:5 to 91 feet below ground surface (bgs).Soil boring locations BS-Ol through BS-05 are shown in Figure 2-1.Three borings were conducted at 1670 Brandywine Avenue and two were conducted at 1690 Brandywine Avenue. I I I I I I I I I I I I I I I I I I I 3.3 MONITORING WELL INSTALLATION The five soil borings (BS-Ol through BS-05)were converted to monitoring wells (MW-Ol through MW-05)following soil sampling activities.A two-inch polyvinyl chloride (PVC) ground-water monitoring well was installed in each boring.Well screens consisted of.. slotted PVC with O.OlO-inch slot size.Well screen sections were 20 feet in all monitoring wells except MW-0 I,in which a 30-foot section of well screen was installed due to a large amount of ground-water rise following drilling activities.All installation procedures were changes in lithology,soil moisture,and organic vapor concentrations.Soil sampling was accomplished using a California Modified 1 3/8"inside diameter split-spoon sampler equipped with three 6-inch brass sleeves.Soil samples were obtained by driving the sampler with a 140-pound hammer dropped from a height of 30 inches in accordance with ASTM D 1586.Two to three split-spoon samples were collected from each boring,for a total of 13 samples.Sample locations were selected to include at least one sample each from the unsaturated and saturated zones. All drilling equipment was decontaminated using a hot-water high pressure washer system prior to the commencement of field activities and between each boring.Field sampling equipment (e.g.,split-spoon samplers,sleeves,caps,etc.)was decontaminated prior to sampling and between each sample using Ogden's standard decontamination procedures, which include a wash in a laboratory grade detergent,potable water rinse,isopropyl alcohol spray,potable water rinse,and distilled water rinse.All decontamination fluids were containerized in DOT approved 55-gallon drums and temporarily stored onsite pending sampling results. 3-2570920144 The ends of the sample sleeves were covered with Teflon tape,capped,labeled,and placed immediately on ice.Headspace vapor analysis was performed as a field screening technique for assessing whether organic contaminants were present in soil samples.This was done by first placing a portion of the soil sample or cuttings into a zip-lock plastic bag. After the bag was allowed to remain in the sun for several minutes,an H_Nu™ photoionization detector (PID)was used to measure organic vapor concentrations within the plastic bag.Soil classification and sampling activities were conducted by a State of California Registered Geologist.Soils were logged using the Unified Soil Classification System (USCS)in accordance with ASTM D 2488.Soil boring logs are included in Appendix A,along with a description of the USCS. I I I I I I I I I I I I I I I I I I I 3.4 GROUND-WATER SAMPLING 3.5 SOIL AND GROUND-WATER SAMPLE ANALYSIS conducted in accordance SA/M Division requirements as specified in the 1996 SAIM Manual.Surface completions for each well consisted of a flush-mounted traffic box finished with a Class A cement surface seal in accordance with SAIM requirements. Monitoring-well construction was overseen by a State of California Registered Geologist. Well construction logs are included in Appendix A. Soil and ground-water samples collected for analysis were delivered with proper chain-of- custody documentation to CKY Inc.Analytical laboratories,in Torrance,California.Soil samples were analyzed for halogenated and non-halogenated VOCs using EPA methods 8010/8020 and for Total Organic Carbon (TOC)using EPA method 90-3.2 ASA.All thirteen soil samples collected were submitted for analysis. 3-3570920144 Ground-water samples were collected from monitoring wells MW-Ol through MW-05 on February 27,1996,in accordance with SAIM Division requirements,following a minimum 72-hour period after monitoring well development.Prior to sampling,depths to ground water were measured and each monitoring well was purged by pumping with a 2-inch Grundfos™submersible pump,which was decontaminated prior to use and between monitoring wells.Purged water was monitored for temperature,pH,and conductivity. Purging was continued until these parameters stabilized with successive measurements. Well development and.purge records are included in Appendix A.Purge water was contained and stored onsite in 55-gallon DOT -approved drums.Ground-water samples were collected from each well with disposable polyethylene bailers. Following installation,each monitoring well was developed in accordance with SAIM division requirements.A surge and bail method was used to develop the monitoring wells. Each well was surged with a surge block for a minimum of 20 minutes,after which ground water was removed with a bailer.Purged water was monitored for pH,temperature, turbidity and electrical conductivity.The process of alternately surging the well and removing ground water with a bailer was continued until the parameters stabilized and until ground water became substantially less turbid.All purged water was drummed in DOT approved 55-gallon drums and temporarily stored onsite.Appendix A contains the monitoring-well development records. I I I I I I I I I I I I I I I I I I I 3.7 HEAT-PULSE FLOW LOGGING 3.6 SURVEYING AND DEPTH TO GROUND-WATER MEASUREMENTS Ground-water samples were analyzed for halogenated and non-halogenated VOCs using EPA methods 8010/8020,and for general chemistry constituents and metals (various EPA Methods).Five ground-water samples were submitted for analysis.Complete copies of original analytica~laboratory reports for soils and ground water are included in Appendix B. Ground-water velocities and flow directions were directly measured in MW-02,MW-03, and MW-04.Ground-water flow measurements were conducted at two different depths in each monitoring well.A minimum of four velocity measurements were collected at each depth and averaged to provide a mean ground-water flow velocity measurement and error range.Measurable ground-water flow was not detected in MW-01 and MW-05.Ground- water flow direction measurements were referenced to magnetic north and subsequently corrected to true north. 3-4570920144 San Diego Land Surveying &Engineering,Inc.was subcontracted to survey the monitoring well elevations.Monitoring wells were surveyed to a vertical accuracy of O.Ol-foot using a bench mark reference to mean sea level.All monitoring wells were surveyed at a notch located at the top of the PVC casing to provide a datum for water-level measurements.Depth to ground water was measured in each monitoring well on February 27,1996,prior to ground-water sampling activities.Ground-water depths were measured with respect to the notch at the top of the PVC casing using a Solinst Model 10 1 water-level meter. Heat-pulse flow (HPF)logging was performed at the subject site on March 12 and 13, 1996,using a Mode1200 GeoFloTM ground-water flow meter.A heat-pulse flow meter is a hydrological logging device used to determine ground-water flow direction and velocity in monitoring wells and open boreholes.A heat-pulse flow meter operates by emitting a heat pulse and measuring subsequent temperature changes in the ground water as a result of the ground-water movement.Direct small-scale ground-water velocity and flow direction measurements can therefore be made within a single well.An article (Gutherie 1986) describing the use of a heat-pulse flow meter is included in Appendix C. I I I I I I I I I I I I I I I I I I I 3.8 MANAGEMENT OF INVESTIGATION-DERIVED WASTE A total of 41 55-gallon DOT~approved drums of investigation-derived waste (lOW)were generated during this investigation.Drum contents include soil cuttings,purge ·water, decontamination water,unused grout,and asphalt.Other lOW,including used tyvek coveralls,nitrile gloves,used headspace bags,and plastic sheeting,were double-bagged,. sealed,and disposed of as municipal waste.Drums were labeled,sealed,and stored temporarily onsite pending analytical results.Details of lOW disposal will be provided in a. separate report. I I I I I I I I I I I I I I 1 I I I I 570920144 3-5 4.1 GENERAL GEOLOGIC CONDITIONS 4.2 REGIONAL GROUND-WATER CONDITIONS SECTION 4 INVESTIGATION RESULTS AND DISCUSSION The closest mapped fault is the La Nacion fault zone.A strand of the La N acion fault zone has been mapped as trending approximately north-south in the general vicinity of Brandywine Avenue adjacent to the eastern edge of the subject site (Kennedy and Tan 1977;Kuper and Gastil 1977).This fault strand is presently considered to show evidence of offset during Quaternary time (last 1.6 million years)but not during Holocene time Jennings 1994). 4·1570920144 According to the Phase II report by CERES (1995),the subject site is underlain by river terrace deposits of Holocene age (less than 11,000 years old).These deposits are underlain by Pliocene-age (less than 5 million years old)deposits of the San Diego Formation Kennedy and Tan 1977;Kuper and Gastil 1977).The terrace deposits are described as unconsolidated sand,gravel,and clay derived from older geologic units.The San Diego Formation consists of yellowish-brown to reddish-brown,fine-to medium-grained marine sandstone. The subject site is located within the Otay Valley Hydrologic Area (HA)of the Otay Hydrologic Unit'of the San Diego Drainage Province (SDRWQCB 1995).Ground water within the Otay HA generally flows from east to west,along the course of the Otay River, toward San Diego Bay.Ground-water quality in portions of the Otay HA is considered to be of poor quality due to high total dissolved solids (TDS)and elevated chloride concentrations.High chloride content may be due partially to the presence of connate water and dissolved salts within marine sediments (Dames and Moore 1989).According to the current Water Quality Control Plan for the San Diego Basin (the Basin Plan),the subject site lies within a portion of the Otay Hydrologic Unit that is designated as having beneficial uses only for industrial purposes;however,discussions with staff at the SDRWQCB indicate.that ground-water beneath the Brandywine site is not exempted from having municipal and agricultural beneficial uses (verbal comm.with Brian McDaniel on May 8, 1996). I I I I I I I I I I I I I I I I I I I 4.4 SITE GROUND-WATER CONDITIONS 4.3 SUBSURFACE SOIL CONDITIONS Ground-water elevations and ground-water contours are shown in Figure 4-1.HPF logging results are discussed in Section 4.6.Ground-water elevations range from 103 feet No hydrocarbon or solvent odors were detected in any of the borings,nor was any visual evidence of soil contamination (Le.,staining,discoloration,etc.)observed.Slight headspace PID readings of 1 to 2 parts per million (ppm)were measured between 36 and 67 feet bgs in BS-04 and at 36 feet bgs in BS-05. 4-2570920144 Ground water was encountered at depths ranging from approximately 52.6 feet bgs in MW-02 to 76.3 feet bgs in MW-04.Ground water rose approximately 10 to 13 feet in MW-Ol,MW-02,and MW-03 within approximately 60 minutes after first being encountered.In contrast,ground water equilibrated at a level approximately 2 feet higher in MW-04 and MW-05 within several hours after boring completion.Ground-water levels in MW-Oland MW-02 recovered relatively quickly subsequent to purging,whereas water levels in MW-03,MW-04,and MW-05 recovered more slowly,as indicated by well purge records (Appendix A). Subsurface conditions encountered during this investigation were generally similar to those described in the previous Phase II subsurface investigation (CERES 1995).Probable fill soils were encountered in the upper few feet bgs of BS-O 1,BS-02,and BS-04.These soils were lithologically similar to the underlying terrace deposits and consisted primarily of moist,brown to light olive brown,silty sand in BS-Ol and BS-04,and dark grayish brown,moist clay in BS-02.Terrace deposits were encountered beneath fill soils in BS-O 1,BS-02,and BS-04,and consisted of brown to dark grayish brown,moist,dense, silty sands and clays.No fill soils were encountered in BS-03.cTerrace-eoeposits encountered in BS-02 were finer grained than in other borings.Cobbly horizons characterized by difficult drilling conditions were encountered at approximately 25 to 37 feet bgs in BS-Ol,28 to 33 feet bgs in BS-02,and 40 to 50 feet bgs in BS-03.The SaIi=Diego-:'Pormation was encountered beneath the terrace deposits at depths ranging from the ground surface in BS-05 to depths of 65 to 70 feet bgs in BS-04.All five borings were terminated within the San Diego Formation,which consisted of moist to wet,dense to very dense,micaceous,olive brown silty sand and silt. I I I I I I I I I I I I I I I I I I I 4.5 ANALYTICAL RESULTS Soil Soil analytical results are shown in Figure 4-3.HVOCs and benzene,toluene,xylenes, and ethylbenzene (BTXE)were not detected above their respective laboratory detection limits in BS-01,BS-02,and BS-05.None of the soil samples collected within the unsaturated zone contained detectable HYOC or BTXE concentrations. Figure 4-2 shows a comparison of ground-water contours at the subject site with ground-water contours at the Omar and Otay Landfill sites.As shown in Figure 4-2, ground-water elevations generally increase toward the northeast,indicating that ground-water flow in the uppermost aquifer is generally southwest. 4-4 The absence of detectable HYOC and BTXE concentrations within the unsaturated zone, relatively high ground-water HVOC concentrations,and a lack of historical and current hazardous materials usage at the site indicate an offsite contamination source.Table 4-1 lists the total organic carbon (TOC)results for soil.These results and their influence on contaminant mobility are discussed in Section 4.7. MSL in the northeastern portion of the site to 93.7 feet MSL in the southwestern portion of the site.Monitoring well recovery data from MW -01,MW-02,and MW-03 (presented in previous paragraph)suggest that the uppermost aquifer beneath the site is somewhat confined (i.e.,under pressure)locally;however,static ground-water elevations across the site indicate that ground-water generally flows from northeast to southwest,as evidenced by the trend of the ground-water contours (Figure 4-1).These results indicate that the subject site is down-gradient of the Omar and Otay Landfill sites.The ground-water gradient (Le.,the slope of the ground-water table)at the subject site is approximately equal to 0.02 ft/ft (106 feet per mile). HVOCs were detected in BS-03 and in BS-04 at depths of 66.5 feet and 86.5 feet bgs, respectively.A trichloroethene (TCE)concentration of 240 Jlg/kg was detected in sample S03D86.5,collected at a depth of 86.5 feet bgs;a TCE concentration of 16 Jlg/kg was detected in S02D66.5 in BS-04,collected at 66.5 feet bgs in BS-04.Both of these samples were collected within the saturated zone (Le.,below the ground-water table). 570920144 I I I I I I I I I I I I I I I I I I I BS..()5~ B~5lEPA Method S01010.0 S02085.5 S05091.0.... 8010 (HVQCs)NO NO NO 8020 (BTXE)NO NO NO w l Z W Wz WAREHOUSE ~ BUILDING c 1670 Brandywine z« Ave.a: co BS-Q4IEPA Method S01026.5 502076.5 S03086.5 8010 (HVQCs)NO NO 1,1 Oichloroethane 15l!glKg Trichloroethene 240 l!glKg 1, 1,2 Trichloroethane 12l!glKg V--Tetrachloroethene 11 l!glKg----- 1, 4 Dichlorobenzene 12l!glKg B5-04 S"------- 1,2 Dichlorobenzene 9l!glKg 8020 (BTXE)NO NO NO - BS.Q3 ~BS-03IEPA Method S01010.5 S02066.5 S03075.5 SHINOHARA LANE ~8010 (HVQCs)NO Trichloroethene 16 l!glKg NO 8020 (BTXE)NO NO NO B~1IEPA Method 501010.0 S02071.0 WAREHOUSE BUILDING V 8010 (HVQCs)NO NO 1690 Brandywine 8020 (BTXE).NO NO Ave. BS-Q2lEPA Method S01011.0 502056.0 "/ V 8010 (HVQCs)NO NO N.0 200BS~1~B5-02~8020 (BTXE)NO NO i ! FEET LEGEND S SOIL BORING LOCATION (BS) OTAY VALLEY ROAD ND NON·DETECT, (VARIOUS DETECTION LIMITS FOR ALL 8010/8020 COMPOUNDS LISTED IN APPENDIX B.NO DILUTIONS NECESSARY) HVOCs HALOGENATED VOLATILE ORGANIC COMPOUNDS BTXE BENZENE,TOLUENE,XYLENES,ETHYLBENZENE SOlO1O.5 SAMPLE NUMBER AND DEPTH BELOW GROUND SURFACE Ilglkg MICROGRAMS PER KILOGRAM BASEMAP:San Diego Land Surveying &Engineering,Inc. I I I I I I I I I I I I I I I I I IOGDENI..... X:\GRAPHICSIBRANDYWINIBASEMAP.FH5 Soil Sampling Analytical Results FIGURE 4-3 Appendix B contains the complete analytical laboratory reports for TOC. Table 4-1 TOTAL ORGANIC CARBON (TOC)RESULTS FOR SOIL I I I I I I I I I I I I I I I I I I I 570920144 Soil Sample BS04S01D26.5 BS04S02D76.5 BS04S03D86.0 BS05S01DlO.0 BS05S04D85.5 BS05S05D91.0 BS01S01D10.0 BSO 1S02D71.0 BS02S01D11.0 BS02S02D56.0 BS03S01DlO.5 BS03S02D66.5 BS03S03D75.5 4·' Total Organic Carbon (TOC) fraction by weight) 0.00079 0.00019 0.00015 0.00027 0.00011 0.00072 0.0021 0.00354 0.00078 0.00059 0.00171 0.00038 0.00032 Ground Water General minerals analytical results for ground water are shown in Table 4-2.Ground water beneath the subject site appears to be of poor quality,with elevated total dissolved solids mS)concentratiot1s ranging from 2,310 to 10,600 milligrams per liter (mg/l)and chloride concentrations ranging from 598 to 5,400 mg/l. The general minerals results for MW-02 differ considerably from the results for the other monitoring wells.Specifically,chloride,sulfate,electrical conductivity (EC),total dissolved solids (TDS)and hardness results are much lower for MW-02 than for MW-01, MW-03,MW-04,and MW-05.These results indicate that the ground water in the vicinity of MW-02 is chemically distinct from other portions of the site.This difference may be a result of influence from an anthropogenic water source,such as over-irrigation of the adjacent landscaping or a leaky irrigation line. The ground-water analytical results for EPA Methods 8010 (HVOCs)and 8020 (BTXE), are shown in Figure 4-4.All five ground-water samples contained detectable concentrations of HVOCs.TCE concentrations in MW':03 and MW-04 are significantly higher than in MW-01,MW-02,and MW-05.TCE concentrations detected in MW-01, MW-02,and MW-05 range from 1.6 to 13 J.1g/l,while concentrations of 400 and 720 J.1g/l were detected in MW-03 and MW-04,respectively.Methylene chloride concentrations in MW-01 through MW-05 ranged from 30 to 87 J.1g/l. 4-8570920144 A comparison of the TCE and methylene chloride ground-water results for the subject site and the adjacent Omar and Otay Landfill sites is shown in Table 4-3.Ground-water analytical data for the Omar and Otay Landfill sites were obtained from available reports on file at the San Diego County SAIM Division. As shown in Table 4-3,the maximum TCE concentrations measured in ground-water beneath the Omar site are substantially higher (by one to two orders of magnitude)than concentrations at the subject site and the Otay Landfill site.Methylene chloride concentrations at the Omar site are also higher than concentrations at the subject site. I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I, I I Table 4-2 GENERAL MINERALS RESULTS FOR GROUND WATER Parameter (units )/EPA Method MW-01 MW-02 MW-03 MW-04 MW-05 MBAS (mg/l)/425.1 0.1 NO 0.76 0.73 NO Turbidity (NTU)/180.1 303 258 3850 684 7240 Alkalinity (mg/l)/31O.l 212 526 450 580 104 Chloride (mg/l)/3oo 4140 598 5400 2450 3330 Sulfate (mg/l)/3oo 1800 358 1320 1800 1020 Nitrate (mg/l)/3oo 5.91 17.4 231 228 8.57 Fluoride (mg/l)/3oo 0.81 1.57 0.77 0.71 0.99 pH/150.1 7.4 7.9 7.3 7.6 7.3 EC (J.unhos/cm)/120.1 11900 3720 16700 10800 9740 TDS (mg/l)1160.1 7900 2310 10600 7820 5800 Color (color units)111O.2 10 10 40 40 10 Odot1140.1 ND NO ND ND ND Hardness (mgIl)1130.2 3960 337 3320 1880 2500 mgn:Milligrams per liter NTU:Nephlometric Turbidity Units MBAS:Methylene Blue Active Substances EC:Electrical Conductivity Ilmhos/cm:Micro-ohms per centimeter IDS:Total Dissolved Solids 570920144 4-9 MW·OS .... MW-GSIEPA Method 501 8010 (HaVCs)Methylene Chloride 30 ugll Trichloroethene 3.0 ug/l 8020 (BTXE)Toluene 1.9 ug/l w Ir-MW-Q4/EPA Method 501 lr 8010 (HaVCs)1,1 Dichloroethene 67 ugll Methylene Chloride 79 ugll cis-1,2-Dichloroethene 11 ug/l 1,1 Dichloroethane 76 ug/l WAREHOUSE V ~ Chloroform 16 ugll BUILDING c 1,2-Dichloroethane 24 ug/l 1670 Brandywine z Trichloroethene 720 ug/l< 1, 1,2 Trichloroethane 47 ug/lAve.C!: lD Tetrachloroethene 56 uall 8020 (BTXE)Benzene 7.1 ug/l V v---MW-03IEPA Method 501 8010 (HaVCs)1,1 Dichloroethene 22 ug/l Methylene Chloride 68 ug/l cis-1,2-Dichloroethene 11 ug/l MW.04~ 1,1 Dichloroethane 60 ug/l MW~/ Chloroform 16 ug/l - 1,2-Dichloroethane 4.3 ug/l Trichloroethene 400 ug/l - 1,1,2 Trichloroethane 31 ug/l Tetrachloroethene 26 uall SHINOHARA LANE 8020 (BTXE)NO V Ir--MW-G1IEPA Method 501 8010 (HaVCs)Methylene Chloride 87 ug/l 13unitWAREHOUSE..8020 (BTXE)NO BUILDING V 1690 Brandywine Ir--MW..Q2IEPA Method 501 Ave./ 8010 (HaVCs)1,1 Dichloroethene 19 ug/l Methylene Chloride 55 ug/l Trichloroethene 1.6 uall 8020 (BTXE) NOMW""~MW....~ LEGEND MONITORING WELL LOCATION (MW) OTAY VALLEY ROAD ND NON-DETECT (DETECTION LIMITS FOR ALL 8010/8020 COMPOUND LISTED IN APPENDIX B. NO DILUTIONS NECESSARY) HVOCs HALOGENATED VOLATILE ORGANIC COMPOUNDS NI'BTXE BENZENE,TOLUENE,XYLENES,ETHYLBENZENE 0 200 i !S01 SAMPLE NUMBER FEET BASEMAP:San Diego Land Surveying &Engineering,Inc. 1lg/1 MICROGRAMS PER LITER I I I I I I I I I I I I I I I I I 1 OGDEN. 1 ••••• X:\GRAPHICS\BRANDYWIN\BASEMAP.FH5 . Ground·water Sampling Analytical Results 4·10 FIGURE 4-4 Table 4-3 COMPARISON OF TCE AND METHYLENE CHLORIDE GROUND-WATER RESULTS WITH ADJACENT SITES Brandywine Distribution Center N/A <1-720 IJ.g/1 <8-87 IJ.g/1 Subject Site) Omar Rendering 0.2 miles east <1-21,000 IJ.g/1 <5-14,000 IJ.g/1 Otay Landfill 0.5 miles northeast <0.1-32 IJ.gll not measured N/A .Not applicable. Brandywine analytical data from results of present investigation and previous Phase II investigation (CERES 1995).Omar Rendering data from Dames and Moore (1995)and Risk-Based Decisions (1996).Otay Landfill Data from IT Corporation (1993)and County of San Diego (1994).Otay Landfill data shown are for uppermost erched)aquifer.. A less-than symbol «)fOllowed by a value indicates the laboratory detection limit. Although both the Otay Landfill and the Omar facility are located upgradient from the subject site,ground-water TeE concentrations beneath the subject site are higher than those detected at the Otay Landfill.In addition,the Omar site is substantially closer to subject site than is the Otay Landfill.Given these observations and analytical results,the Omar site represents a more likely source of ground-water contamination at the subject site than does the Otay Landfill. Range of Methylene Chloride Concentrations in Ground Water2 Range of TCE . Concentrations in Ground Water2 4-11 Distance and Direction from Subject Site Analytical results for metals are shown in Table 4-4.These results,which are for unfiltered ground-water samples,also indicate poor ground-water quality.Table 4-5 shows a comparison of selected metal concentrations in ground water from the subject site with available analytical data from the nearby Omar and Otay Landfill sites.Maximum ground-water metal concentrations generally appear to be higher at the subject site than at the Omar and Otay Landfill sites;however,direct comparisons of metal concentrations among the three sites listed in Table 4-5 are not possible due to varying levels of suspended solids in ground-water at the three sites.Typically,high levels of suspended solids in ground water result in increased total metal concentrations.The main conclusion to be 570920144 I I I I I I I I I I I I I I I I I I I I I Table 4-4 I METALS RESULTS FOR GROUND WATER I Element (units)/EPA Method MW-Ol MW-02 MW-03 MW-04 MW-05 I Antimony (J.lg!l)/3OO5 <60 <60 <60 <60 <60 Arsenic (J.lg!l)/3OO5 <100 <100 171 <100 303 I "'-.,Barium (J.lg!l)/3OO5 284 37.8 762 196 1,480 Beryllium (J.lg!l)/3OO5 <5 <5 <5 <5 6.41 I Cadmium (J.lg!l)/3OO5 <5 <5 <5 <5 <5 Calcium (J.lg!l)/3OO5 791,000 79,800 725,000 433,000 519,000 Chromium (J.lg!l)/3OO5 67.7 <10 266 54.3 701 I Cobalt (J.lg!l)/3OO5 16.4 <10 111 36.9 160 Copper (J.lg!l)/3OO5 51 <10 129 30.1 255 I Lead (J.lg!l)/3OO5 <100 <100 158 <100 230 Magnesium (J.lg!l )/3005 481,000 33,400 366,000 195,000 291,000 I Mercury (J.lg!l)n470 <0.2 <0.2 0.54 0.28 5.·13 Molybdenum (J.lg!l)/3OO5 73.9 <50 <50 <50 <50 I Potassium (J.lg!l)/3OO5 40,100 3,670 62,700 21,400 114,000 Nickel (J.lg!l)/3OO5 37.5 <20 325 217 182 Selenium (J.lg!l)/3OO5 <200 <200 <200 <200 3,590 I Silver (J.lg!l)/3OO5 <10 <10 <10 <10 <10 Sodium (J.lg!l)/3OO5 1,110,000 605,000 268,000 1,620,000 1,380,000 I Thallium (J.lg!l )/3005 <500 <500 1,440 <500 2,540 Vanadium (J.lg!l)/3OO5 115 29.1 647 111 1,010 I Zinc (J.lg!l)/3OO5 440 38.4 1,290 482 4,220 I A less-than symbol «)followed by a value indicates the laboratory detection limit. I I I I 570920144 4-12 A less-than symbol «)followed by a value indicates the laboratory detection limit. Table 4-5 Notes: I From Dames and Moore (1989).Metal concentrations converted from parts per million. 2 From IT (1993).Metal concentrations converted from mgll. COMPARISON OF SITE GROUND-WATER METAL CONCENTRATIONS WITH GROUND-WATER DATA FROM THE OMAR AND OTAY LANDFILL SITES 4-13570920144 Range of Range of Range of Ground-water Ground-water Ground-water Concentrations at Concentrations Concentrations at Element Brandywine Site at Omar Site I Otay Landfl11 2 Arsenic (J.1g/l)<100-303 <30-140 <10-17 Barium (J.1g/l)37.8-1,480 <40-220 <200-440 Chromium (J.1g/l)<10-701 <10-70 <10-600 Lead (J.1g/l)<100-230 <8-12 <10-80 Mercury (J.1g/l)<0.2-5.13 <3.3-7.3 <0.2-0.4 Selenium (J.1g/l)<200-3,590 <16-42 <10-27 Thallium (J.1g/l)<500-2,540 <60-540 <10-430 I I I I I I I I I I I I I I I I I I I 4.6 REAT-PULSE FLOW LOGGING RESULTS drawn from Table 4-5 is that elevated metal concentrations occur in the ground water beneath all three sites. One explanation for the vertical variability of flow directions and velocities measured in MW-02 is that since HPF measurements are made at a point source (Le.,a particular level in a small-diameter monitoring well),such measurements may reflect localized flow irregularities through the aquifer material rather than regional ground-water flow directions. A northeast ground-water flow of approximately 3 feet per day was measured at 49 feet bgs in MW-02,whereas a southward flow of approximately 11 feet per day was measured at 44 feet bgs in MW-02.These results may reflect localized influence from an anthropogenic surface water source,as discussed in Section 4.5.Alternatively,these results may reflect a natural variability of the overall ground-water flow field,as discussed below. 4-14 HPF logging results are presented in Table 4-6 and Figure 4-1.Ground-water flow directions and velocity measurements obtained from HPF logging are considered approximate due to variability in the HPF data;however,these results are generally consistent with ground-water flow directions indicated by the trend of the ground-water contours (also shown in Figure 4-1).The HPF data and the ground-water contours both indicate that ground-water beneath the subject site flows in a southwest to northwest direction.Vertical1~ability of the ground-water flow field was also observed,as is typical for many aquifers (Fetter 1988). The results from MW-03 indicate a southwest flow direction of approximately 3.9 to 13.9 feet per day,with an average value of approximately 8.9 feet per day.HPF logging results indicate that ground-water flow in the vicinity of MW-04 is generally west to northwest at velocities ranging from approximately 2.7 to 4.3 feet per day,with average values of 3.5 to 4.1 feet per day.No measurable flow was detected in MW-Ol and MW-05,located in the southern and northern portions of the site,respectively.Based on the flow meter instrument sensitivity and on site ground-water conditions,ground-water flow in the direct vicinity of these wells is estimated to be less than about 1 foot per day. Measured ground-water flow directions in each monitoring well generally exhibited 10 to 30 degrees of variability,and ground-water flow velocity measurements generally exhibited approximately 0.2 to 5 feet per day of variability. 570920144 I I I I I I I I I I. I I I I I I I I I 4.7 RESULTS OF CONTAMINANT MOBILITY EVALUATION Such flow irregularities can result from locally heterogeneous aquifer conditions such as changes in lithology,which cause significant changes in hydraulic conductivity.Flow variability in MW-02 may therefore be a result of preferential groundwater flow at discrete depths in the direct vicinity of MW-02. As a rough check of the HPF ground-water velocity results,hydraulic conductivities were back-calculated for aquifer materials from HPF data and from the measured ground-water gradient (Le.,the slope of the water table)beneath the subject site.Hydraulic conductivity K)is a measure of the rate at which water moves through a permeable medium. Calculated hydraulic conductivities range from 0.014 to 0.073 centimeters per second cm/s).These values are within a typical K range of 0.0001 to 0.01 for silty sand (Fetter 1988).Measured ground-water velocities at the subject site therefore appear to be realistic values. Ground-water elevations and heat pulse flow data indicate an overall westward ground- water flow direction in the direct vicinity of MW -03 and MW -04.HPF data indicate that the most significant ground-water flow is primarily occurring beneath the central portion of the site,as indicated by generally higher flow velocities and more consistent flow directions in this area than in the northern and southern portions of the site (Figure 4-1).Ground- water TCE concentrations are also higher in this portion of the subject site than in the northern and southern portions of the site.This portion of the site is directly down- gradient of the adjacent Omar site;therefore,the Omar site represents the most likely source of ground-water contamination observed at the subject site. 4·16570920144 The mobility of TCE in ground-water beneath the subject site and vicinity was evaluated by calculating its retardation factor (R).R represents the degree to which the average velocity of a dissolved contaminant plume in ground water is retarded (Le.,slowed down)relative to the ground-water flow velocity.The larger the R value,the slower the average velocity of the contaminant plume relative to that of the seepage velocity (Le.,the velocity of ground water).R is strongly influenced by the fraction of organic carbon (TOC)in the aquifer material.The higher the fraction of TOC in the aquifer material,the lower the mobility of an organic contaminant,since organic compounds exhibit a strong tendency to sorb onto organic carbon particles within an aquifer (Fetter 1993). I I I I I I I I I I I I I I I I I I I Discussion of Contaminant Mobility Results The retardation factor (R)is defined by the following equation: where Kd =the distribution coefficient; Bd =the bulk density of the aquifer material (assumed to equal 1.3 kg/l);and aff =the effective porosity of the aquifer material (assumed to equal 0.3). Two methods were used to estimate Kd for TCE.The first method used the soil and ground-water analytical results presented in Figures 4-3 and 4-4 to calculate Kd values of approximately 0.04 liters per kilogram (lIkg)and 0.33 lIkg from MW-03 and MW-04 data, respectively (see Table 4-7). Equation 4-2;Fetter 1988) 4-17 R=1+KdBd eeff TCE plume travel times from the Omar site to the subject site were estimated to be relatively low (0.4 to 2.7 years);therefore,not much time would be required for a TCE plume originating at the Omar site to migrate to the subject site.Historical TCE concentrations as high as 3,000 J.1g/l have been measured in ground water beneath the Omar site (Table 4-3). Methylene chloride concentrations as high as 14,000 J.1g/l have also been measured (Dames and Moore 1995). As explained below,average TCE plume velocities (i.e.,retarded velocities)derived from estimated R values are relatively close to measured ground-water velocities.This indicates that the dissolved TCE ground-water plume beneath the subject site is relatively mobile, since its average velocity is close to that of the ground water.As noted above,aquifer materials contain very little organic carbon,indicating high TCE mobility. 570920144 The distribution coefficient (Kd)in Equation 4-2 is a measure of the equilibrium partitioning of a compound between the sorbed and dissolved phases.A site-specific Kd value can be estimated by dividing the TCE concentration in soil by the TCE concentration in ground water at the subject site.Bulk density (Bd)and effective porosity (an-)values were estimated from typical ranges for these parameters given by Holtz and Kovacs (1981)and Fetter (1988). I I I I I I I I I I I I I I I I I I I Table 4-7 provides a summary of the estimated Kd values for MW-03 and MW-04 obtained by the two methods described above. Dividing the estimated TCE plume velocities in Table 4-8 by the distance from MW-03 and MW-04 to the former Omar evaporation ponds (a distance of 1,000 to 1,500 feet)yields average plume travel times ranging from 0.4 to 2.7 years.This result indicates that a relatively short time period would be required for a TCE plume originating at the Omar site to migrate to the subject site relative to the elapsed time since 1978,when the Omar site stopped receiving hazardous wastes. Table 4-8 provides a summary of estimated R values using the Kd estimates shown in Table 4-7.The estimated R values shown in Table 4-7 are relatively low,suggesting that TCE jn ground water beneath the subject site and vicinity is relatively mobile.Dividing the· measured ground-water velocities in MW-03 and MW-04 by the estimated R values shown in Table 4-7 gives the average velocity range of the TCE contaminant plume beneath the subject site.TCE plume velocity estimates are approximately equal to the.average ground- water velocities measured in MW-03 and MW-04,indicating very little retardation of the TCEplume. The second method estimated Kd values based on a published relationship between the organic carbon/water partitioning coefficient (KoC>and the octonol/water partitioning coefficient (Kow).Kd is equal to the Koc value for the compound times the organic carbon fraction (Fetter 1988).The higher the organic carbon fraction of the soil,the greater the tendency of the organic compound to sorb onto the soil rather than remain in the ground water,and thus the lower the mobility of the compound in ground water.The TOC results shown in Tables 4-1 and 4-7 provide a measure of the organic carbon fraction present in soil samples from MW-03 and MW-04.Kd values estimated for TCE were calculated based on a published K ow .value for TCE (Fetter 1993)and an empirical relationship between K ow and Koc (Karichoff et al.1979). 4-18570920144 I I I I I I I I I I I I I I I I I I I ESTIMATED R VALUES AND TeE PLUME VELOCITIES I Based on a published Kow value for TCE (Fetter 1993)and an empirical relationship between Kow and Koc by Karichoff et aI.(1979)(Koc=O.63Kow). Range of Estimated Estimated Average R values Velocity Range of TCE Average Ground-Water Velocity Monitoring Well (Equation 4-2)Plume (From HPF Data) MW-03 1.2 7.4 ftIday 8.9 ftIday MW-04 1.1-2.4 1.5-3.7 ftIday 3.5-4.1 ftIday Kd TCE Estimated Range of TCE Concentration from TOC Estimated KdDerived Monitoring Concentration "in Ground Analytical Results Koc from Estimated Well Soil Warer Data (percent)for TCE1 Koc MW-03 16 Ilg/kg 400 Ilgll 0.04l1kg 0.032-0.17 123 0.04-0.21 lIkg MW-04 240 Ilg/kg 720 Ilgll 0.33 lIkg 0.015-0.079 123 0.02-0.10 lIkg 4·19 Table 4-' Table 4-8 SUMMARY OF ESTIMATED Kd VALUES 570920144 I I I I I I I I I I· I I I I I I I I I 2.No detectable concentrations of contaminants were observed in site soil within the unsaturated zone. SECTION 5 SUMMARY AND CONCLUSIONS 3.There is no evidence of historic or current hazardous materials storage,use,or release at the site.Therefore,an offsite source of the detected contamination is indicated. 5.HPF logging results indicate that ground-water flow beneath the subject site appears to be generally in a westward direction.Results from MW-03 indicate a southwest flow 5-1 I.Ground-water analytical results indicate elevated HVOC concentrations beneath the central portion of the subject site.TCE concentrations of 400 and 720 Ilgn were measured in ground water samples collected from MW-03 and MW-04,respectively. In contrast,MW-Ol,MW-02,and MW-05 analytical results for ground water displayed much lower HVOC concentrations ranging from 1.6 to 13 Ilg/l. A limited ground-water and soil investigation was conducted at the Brandywine Distribution Center,located at 1670 and 1690 Brandywine Avenue in Chula Vista, California.The investigation was conducted on behalf of Chula Vista Industrial Realty, Inc.to verify the presence of ground-water contamination beneath the subject site,evaluate ground-water flow direction,velocity,and gradient,and determine potential sources of the identified contamination. The investigation included completion of soil borings,installation and sampling of ground- water monitoring wells,analytical testing of soil and ground-water samples,heat-pulse flow logging,geochelnical evaluation of ground water,and report preparation.The following conclusions have been developed as a result of this investigation: 4.Review of available records indicates that the Hyspan property,located adjacent to the subject site on the eastern side of Brandywine Avenue,does not appear to be a possible source for HVOCs detected in ground water at the subject site.Similarly,HVOC concentrations detected in ground water at the Otay Landflll are lower than those at the subject site;therefore,the Otay Landfill also does not appear to be a likely source of ground-water impacts at the subject site. 570920144 I I I I I I I I I I I I I I I I I I I No evidence indicates that ground-water contamination at the subject site has originated frQm an onsite source.The most likely source for contamination of ground water beneath the subject site appears to be the adjacent Omar site. 8.Review of the previous Phase I and Phase II reports for the subject property and review of SAIM Division files indicates that ground-water contamination has been extensively documented beneath the Omar site,with TCE and methylene chloride concentrations in ground water as high as 21,000 and 14,000 J.1g/l,respectively. direction of approximately 3.9 to 13.9 feet per day in the east-central portion of the site, with an average value of approximately 8.9 feet per day.HPF logging results also indicate that ground-water flow in the vicinity of MW-04 is generally west to northwest at velocities ranging from approximately 2.7 to 4.3 feet per day. 6.Direct measurements of ground-water flow direction in the vicinity of MW-03 and MW-04 are generally consistent with the overall direction of the hydraulic gradient. Both lines of evidence indicate an overall westward ground-water flow direction beneath this portion of the subject property.This portion of the subject property displays the highest TCE concentrations in ground water and appears to be located directly down-gradient of the adjacent Omar site. 5-2 7.TCE in ground water beneath the subject site and vicinity is relatively mobile,as evidenced by low retardation factor (R)values and estimated TCE plume velocities approaching average estimated ground-water flow velocities.Estimates of the ground- water travel time between the Omar and subject sites suggest that a TCE plume originating at the Omar site could migrate to the subject site within a relatively short. time period (approximately 0.4 to 2.7 years). 570920144 I I I I I I I I I I I I I I I I I I I SECTION 6 RECOMMENDA TIONS No further site assessment activities are warranted at the subject site.There is no evidence of the storage,use,-or release of hazardous chemicals at the site.The results of soil and ground-water testing indicate that the ground-water contamination observed onsite is a result of migration from an upgradient,offsite source or release.To be effective,potential ground-water remediation activities would have to be initiated at the offsite contaminant source rather than at the subject site. Ogden recommends that this report be submitted to the SDRWQCB.They are currently compiling and evaluating data associated with the known ground-water contamination in the area (per.comm.with Mark Alpert,April 1996).Following SDRWQCB review of this report,it is recommended that Ogden meet with the SDRWQCB on behalf of Chula Vista Industrial Realty,Inc.to discuss the results for the subject site and to request a "no further action"letter specifying that the observed ground-water contamination is not due to former or current site uses or activities and is the result of the migration of releases from offsite sources.Ogden Environmental can assist in this effort as requested. I I I I I I I I I I I I I I I I I I I 570920144 6-1 I I I- I I I I I I I I I I I I I I I I SECTION 7 REFERENCES BEM Systems, Inc. 1994. · Phase I Environmental Site Assessment, Brandywine Distribution Center, 1670 & 1690 Brandywine Avenue, Chula Vista, California. Prepared for-Citicorp Real Estate, Inc., Dallas, Texas. CERES Environmental. 1995. Phase II Subsurface Soil Assessment, Brandywine Distribution Center, 1670 and 1690 Brandywine Avenue, Chula Vista, California. Prepared for Chula Vista Realty, Inc., Los Angeles, California. County of San Diego 1994. Final Closure and Postclosure Maintenance Plan, Otay Sanitary Landfill (Class ill Portion), prepared by Department of Public Works, May. Dames and Moore. 1989. Site Investigation, Former Omar Rendering Facility, Chula Vista, California. For Darling Delaware Company, Inc. June. Dames and Moore. 1995. Annual Groundwater Monitoring Report, Monitoring Record 1994, Omar Rendering Site, 4826 Otay Valley Road, Chula Vista, California. Prepared for Darling Delaware International, Inc. January. Department of Environmental Health, County of San Diego, Site Assessment and Mitigation (SNM) Division. 1996. Site Assessment and Mitigation Manual. Fetter, C.W. 1988. Applied Hydrogeology. Macmillan Publishing Company, New York, New York. Fetter, C.W. 1993. Contaminant Hydrogeology. Prentice-Hall, Inc., Upper Saddle River, New Jersey. Freeze, R.A. and Cherry, J.A. 1987. Groundwater. Prentice-Hall, Inc., Englewood Cliffs, New Jersey. Gutherie, M. 1986. Use of a Geo Flowmeter for the Determination of Ground Water Flow Direction. Ground Water Monitoring Review. Vol. 6, No. 1. Holtz, R.D. and Kovacs, W.D. 1981. An Introduction to Geotechnical Engineering. Prentice-Hall, Inc., Englewood Cliffs, New Jersey. IT Corporation. 1993. Report of Disposal Site Information, Otay Annex Sanitary Landfill. Prepared for County of San Diego Department of Public Works. June. IT Corporation. 1995. 1994 Annual Report. Chapter 15 Detection Monitoring Program, Otay/Otay Annex Landfill. February. Jennings 1994. Fault Activity Map of California and Adjacent Areas. California Division of Mines and Geology, California Geologic Data Map, Map No. 16. Karichoff, S.W., Brown, D.S., and Scott, T.A. 1979. Sorption of Hydrophobic Pollutants on Natural Sediments. Water Research. Vol. 13. 570920144 7-1 I I I I I I I I I I. I I I I I I I I I Kennedy, M.P., and S.S. Tan. 1977. Geology of National City, Imperial Beach and Otay Mesa Quadrangles, southern San Diego Metropolitan Area, California. California Division of Mines and Geology Map Sheet 29, Scale: 1 :24,000. Kuper, H.T., and G. Gastil, 1977. Reconnaissance of marine sedimentary rocks of southwestern San Diego County, in Farrand, G., ed., Geology of Southwestern San Diego County, California and Northwestern Baja California, San Diego Association of Geologists Guidebook. Risk-Based Decisions, Inc. 1996. Addendum to Site Investigation and Risk Assessment for the Former Omar Rendering Site, Chula Vista, California. Prepared for Darling International, Inc. San Diego Regional Water Quality Control Board (SDRWQCB). 1995. Water Quality Control Plan for the San Diego Basin (Region 9). 570920144 7-2 I I I I I I I I I I I I I I I I I I I SECTION 8 LIMITATIONS The data presented in this report are intended for use in the course of a site investigation. The data cited herein should not be used for other than its intended purpose. Furthermore, Ogden's conclusions are based solely on these data. Changes in the condition of the project site may occur with time due to either natural processes or human activities. The site investigation was carried out using the degree of care and skill ordinarily exercised under similar circumstances by qualified professionals; no further warranty is made. 570920144 8-1 I I I I I I I I I I I I I I I I I I I APPENDIX A DESCRIPTION OF uses AND BORING/MONITORING WELL LOGS ULS REPORT WELL DEVELOPMENT AND GROUND-WATER SAMPLING LOGS I I I I I I I I I I I I I I I I I I I DESCRIPTION OF uses AND BORING/MONITORING WELL LOGS I I I I I I I I I I I I I I I I I DEFINITION OF TERMS PRIMARY DIVISIONS SYMBOLS SECONDARY DIVISIONS GRAVELS CLEAN GW Well graded gravels, gravel-sand mixtures, little or no fines GRAVELS More Than (ussThan a, ii Half of &%Fines) GP Poorly gra~ gravels, gravel-sand mixtures, little or no fines cg Coarse ij~ Fraclion is GM Silty gravels, gravel-sand-silt mixtures, non-plastic fines Larger Than GRAVEL ffi-~ G> No. 4 Sieve With Fines z O Ii~ GC Clayey gravels, gravel-sand-clay mixtures, plastic fines i!i=t CLEAN SW WeU graded sands, graveUy sands, little or no fines ~ JJJl SANDS SANDS I- More Than (Less Than cj-Half of &%Fines) SP Poorly graded sands, gravelly sands, little or no fines 8 ·-Coarse Fraclion is SM Silty sands, sand-silt mixtures, non-plastic fines Smaller Than SANDS No. 4Sieve With Fines SC Clayey sands, sand-clay mixtures, plastic fines Ill Inorganic silts, rock flour, fine sandy silts or clays, and clayey silts j~ SILTS AND CLAVS with non-or slightly-plastic fines Liquid Limit is CL ln:l,anic c1ay: of low to medium plasticity, gravelly clays, silty clays, 51::!o Less Than 50o/o san clays, an clays z G> Q o c~ OL Organic silts and organic silty clays of low plasticityw-£ z iii G> : c~ ' ._H Inorganic silts, micaceous or diatomaceous fine sandy or silty soils, a: i l cij elastic silts, clayey siltC,.c-SILTS AND CLAVSw1-i j~ Liquid Limit is CH Inorganic clays of high plasticity, fat clays Greater Than 50% OH Organic clays of medium to high plasticity, organic silts HIGHLY ORGANIC SOILS Pt Peat and other highly organic soils GRAIN SIZES SILTS AND CLAVS SAND GRAVEL I I cqARSE I COARSE COBBLES BOULDERS FINE MEDIUM FINE 200 40 10 4 314• 3" 12" U.S. STANDARD SERIES SIEVE CLEAR SQUARE SIEVE OPENINGS RELATIVE DENSITY CONSISTENCY SANDS, GRAVELS CLAYS ANDANDBLOWS/FOOT* BLOWS/FOOT* NON-PLASTIC SILTS PLASTIC SILTS *NUMBER OF BLOWS OF 140 POUND HAMMER VERY LOOSE 0-6 VERY SOFT 0-3 FALLING 30 INCHES LOOSE 6-14 SOFT 3-6 TO DRIVE A 3 INCH 0.0. MEDIUM DENSE 14-43 FIRM 6-12 (2 INCH 1.0.) SPLIT SPOON DENSE 43-71 STIFF 12-23 VERY DENSE >71 VERY STIFF 23-46 HARD >46 I OGDEN FIGURE Unified Soll Classlflcatlon System I ••••• I OGDEN BORING LOG Page f of 5 I I I I I I I I I I I I I I I I I I cLIEN T ____;;Ccc.h-=-ul-=-a --'-V'-=-is..:..:ta=-I=-n-'-d.;_us--'-tr_ia=-I_R-=-ea-=-l=tY.:...., -=-In'-=-c---. -------BORING NUMBER _B_S_-/vf_W_O_I _________ _ PROJECT NAME/NUMBER-Brandywine Dist. Ctr, NO. 570920144 COMPLETION DEPTH _7_1_ft_. -------------- DA TE/TIME ST AR TED _0..::.2_-1_7_-9:....:6'--'/--=-08=---l-=-5 _______ _ BOREHOLE DIAMETER _8_" ______________ _ DATE/TIME FIN !SHED --'-0..::.2_-1---7_-9:....:6'--'/'---'-=I0--'4-=-0 _______ _ DRILLER/COMPANY _R_us_s_!_V_a_lle--'-y_W_e_ll __________ _ COORDINATES _N...:...I_A,'---------------DRILLING METHOD/FLUID ___:.__H:..:.o:.:..:llo:..:.cwc...:S=-=t..::.e:c:..m:.:..:A..::.ug""e:.:.r ________ _ ELEVATION AND DATUM--------'-...__ _______ _ DRILLING EQUIPMENT _F...c:a ___ ilin__,g._F_--=6=------------- TOP OF CASING ELEVATION 141.48 GEOLOGIST D Barrie CHECKED BY J Jones I-w (.') enz0 w >-wa: ::::> u -' en I a: <-< I1---' _,w 0 a..E u -' WELL 1--a.. a., a.. w a.. CD u en a. u DESCRIPTION a.. a., w~ ::E > ::E::E 0 a. I DIAGRAM w~ < 0 <::::> :;: a.. -' 0 en u enz 0 <-< 0 0 w -' w a: a: CD I (.') en - Asphalt at surface 11::: ~lsi:i ~ K1-I"'-K H I"'-K ~ I"'-K 2-I"'-K ._2 K I"'-~ ~ 3-I"'--._3 I"'-K I"'-K ~ I"'-~ H4-I"'-I" I" ~ I"' I" 5-SILIY SA~D fine-to medium-grained I"'-~ ~s sand, probable fill (75% sand, 25% fines) I"'- I"'-~ 6-(J I"'-I" f----6 ::,. I"'-I" Cl.. c::, K I" ~ q- Lu I"'-~ .... 7-~ ~7 :5 ~ c::, c:::, cc I"-~ 2 lj SM (/) K K 8-. K ~ -8ALLUVIUM/TERRACE DEPOSITS ' K - K 9-K -9K "' - K "' -.. K "' 10-BWBS01S01D11.0 15 0.0 SILIY SA~D brown 10YR4/3, moist, dense, K ~ ---10 X fine-grained (75% sand, 25% fines) K - I -25 K "' 11-25 K K HI IX K K -~ "' K ~ 12-"' K ---12 K K K K 13- K K --- 13KI" K K K K 14-r---' --1-14 ~ -- I OGDEN BORING LOG Page 2 of 5 BORING NUMBER _B_S_-M_W_O_! _________ _ I C:E; :hu= Vi:a Industrial Realty, Inc. PROJECT NAME/NUMBER-Brandywine Dist Ctr NO 570920144 COMPLETION DEPTH 71ft I I I I I I I I I I I I I I I I I I ,_- Cl.. (lJ w~ 0 15- 16- 17- 18- 19- 20- 21- 22- 23- 24- 25- 26- 27- 28- 29- 30·-=- a"1 w a: _J Cl.. w :::.: > t 0 Cf) u w a: I-w (!) Cf) z u 0 Cf) wa: _J ::::, < t-·,c,: -' W 0 Cl.. E u _J Cl.. CD u Cf) a. u :::.: :::.: 0 a. I <t::::, 3: Cl.. _J Cf) z 0 ..,:-t J ·tn a: 0 CD I (!) Cf) SM 1-. -o-5.M. DOQ SC 0 oc oOO 0 oc D00 0 oc D oo 0 oc Doo 0 · oc D oo 0 oc D oo 0 oc D oo 0--0 E -- I WELL ,--DESCRIPTION Cl.. (lJ DIAGRAM w~ 0 I"" I"" I"' ~ .... I"' H5I"-I"' I"' H6 I"- H7 "" "" "" "" "' "" - 18 "' "' I"" "" - I"" "" "" '" - H9 SILTY SAND same as above "" ~ ',--20 I"' "" - I"' "" '-21l.l I"" "" :,. c:, -' I" "" I"' Lu I"' :::, s c:, -22 c::i I"' Cl:: t!) l.l "" I"' .... VJ I"' "" -23 "" "" "" "' .... 24 "' "" "' "" .... Abundant cobbles "' "" >--25 I"- e-26 "' "' "" ~ I"" -27 I"" "" I"" "" "" "" "" "" - 28 29 I"' ~ '"" ------. -- e-30 -- I OGDEN BORING LOG Page 3 of 5 ----- I CLIENT Chula Vista Industrial Realty, Inc. BORING NUMBER as:...uwot PROJECT NAME/NUMBER-Brandywine Dist. Ctr, NO. 570920144 COMPLETION DEPTH 71 ft. I 11'1 I-w (!) (flzu0 (fl >-wo:: -' I w 0:: ::> <(~ <( I1---' -'W 0 Cl.. E u -' WELL I--Cl.. (1) Cl.. .w Cl.. CD u (fl a. u DESCRIPTION Cl.. (1) w~ ::E > ::E ::E D a. I DIAGRAM w~ <( 0 <( ::> 3: Cl.. -' D (fl u CJ'lZ 0 <(-D I w -' -~ 0:: 0 0:: CD (!) CJ') S.M. SILIYLCLAYEY SAND ~III:! GBAl.!EL darkSC grayish brown 10YR4/2, moist. dense, low I plasticity, very difficult drilling, rock >-:::, 31310.0 fragments composed of gray fine-grained a fl: metavolcanic (?) rock (25% gravel, 60% (.!) sand, 15% fines) tI32 32 I 33 ~ 33 _, t.) i's e=; 0.. ::,. 34 a <'. 34I 't UJ lJ.J 5 Cl 35 ~ 35 I t.) V) 36 36 I 37 SILIY SAND ~III:! GBAl.!EL dark grayish 37 I brown 10YR4/2, moist, dense, gravel is composed of metavolcanic (?) and granitics 38 ( 40% gravel, 40% sand, 20% fines) 380.0 I 39 39 I 40 ~ 0 .... SM SAN DIEGO FORMATION <,: V) I SILIY SAND olive brown 2.5Y 4/3, moist, no ~ 41 plasticity, micaceous, fine-grained (85% "" .... sand. 15% fines) ~ UJ 5 I V) 242 ~ 0.. Cl ~ 3I 43 a _, V) S? a c:i 44 4 I 45 5 I ·------ 46 --------6 -------- I I OGDEN BORING LOG Page 4 of 5 ----- I CLIENT Chula Vista Industrial Realty, Inc. BORING NUMBER 85-MWOI PROJECT NAME/NUMBER Brandywine Dist. Ctr, NO. 510920144 COMPLETION DEPTH 11 ft. I <l"1 f-w (!) enzu0en >-w er: _J I w er: ::) <-·<[ If--_J -'w 0 a.. E u _J WELL f--a.. QJ a.. w a.. CD u en o. -u DESCRIPTION a.. QJw2 :::;: > :::;: :::;: 0 Q. I DIAGRAM w2 <( 0 <(::) 3' a.. _J0enuenz0 <(-0 I w _J ·l!:I er: 0 er: CD I (!) en SM I 47 I 48 J I 49 I 50 100 25 0.0 SILT WITH SAND olive brown 2.5Y 4/ 4, moist, hard, micaceous, low plasticity (15% 35 ML sand, 85% fines) 51 SlLLdark gray 2.5Y 4/1, moist, hard, . 1 45 micaceous, low plasticity, low dry strength 10% sand, 90% fines) 52 I as53lJJ 5 I (/) 2 ~ Cl.. "< 54 @ (/) f,..: ' ..... "' I C) 'II, ..... 55 100 20 0.0 SlLLdark gray 2.5Y 4/1, same as above ~ C) c:i I 35 56 50 I 57 I 58 I 59 9 I 60 83 17 0.0 SILT WITH SAND dark gray 2.5Y 4/1, same 0 as above with slightly higher percentage of '¥ 20 sand, driller reports that center plug is 61 slightly wet (15% sand, 85% fines) I 25 52-~------2 ----- I I OGDEN -----BORING LOG Page 5 of 5 I CLIENT --=C:.:..:h..:..ul.::.a....:V..:.:is:..:.fa=-..::.:In....:d:.:u..:..s:.:...tr:.::ia~I-' R:.:..:e:..:a:.:..:lf;.,.Y'-, I::.:..nc::.c'-. ______ _ BORING NUMBER _B_S_-M_W_O_I _________ _ I I I I I I I I I I I I I I I I I PROJECT NAME/NUMBER Brandywine Dist Ctr NO 570920/44 COMPLETION DEPTH 71ft ii'! f-w (.9 Cf) z u 0 Cf) w >-wo: ~ I a:: ::::> <t--<t f--~ ~ w 0 a.. E u ~ a.. QJ a.. w a.. CD u Cf) Q. :r: u DESCRIPTIONw1! :::;: > :::;: :::;: 0 Q. <t 0 <t ::::> 3: a.. ~ 0 (f) u (f) z 0 < t- t 0w ~ ·Lei 0: 0: CD I (.9 (f) ML 63- 64- 65-88 10 0.0 SILT WITH SAND TO SILTY SAND same as X above, driller reports that center plug is 25 dry (15% sand, 85% fines) ll 66-~ ll 50 67- 68- 69- 70-~ BWBS01S02D71.0 20 SILT WITH SAND TO SILTY SAND same as IX above but wet, free water present. water I 37 rose to 60 feet in 5 minutes 71-BORING COMPLETED TO 71 FEET BGS0.0 SET MONITORING WELL, GROUNDWATER FIRST ENCOUNTERED AT 60.5' BGS, 72-GROUNDWATER AT 48.J'BGS AFTER 4 HOURS 73- 74- 75- 76- 77- 73-:.... ---------·---- I WELL f--a.. QJ DIAGRAM w1! 0 Hl3 . 1---~ L-- L-- Hl4 . L-- L-- CJ -~ Lu - 5 --(/) -- 65 ~ --"----~ _. I: -(/) - f----~ - 66a -'- vj . '--. (\J a '-- iS '-- c:i '-- 67 '---··'-- L---·. 1-- Hl8 '--1-- 1-- Hl9 -- 70 71 72 73 74 75 76 77 78 I OGDEN BORING LOG Page I of 4 I I 1 I I I I I I I I I I I I I I CLIENT _...;C_h_ul_a_V_is_ta_;...In_d"'""us=-tr_ia"--I_R_e_al_.ty""", _In_c_. -------BORING NUMBER __;B::::c.=.S_-;....;.M-'--'.W....::.0='2 _________ _ PROJECT NAME/NUMBER Brandywine Dist. Ctr, NO. 570920144 COMPLETION DEPTH --=5..::.6.:.:..S_f..:..:t. _____________ _ DA TE/TIME ST ART ED _0_2_-_17_-"'""96---'-/--=12..:..5.c...5 _______ _ BOREHOLE DIAMETER --=8=-"--------------- DATE/ TIME FIN ]SHED _0_2_-_17_-.;....96---'-!_14--=2..:..0 __ --'------- CO ORO INA TES _N_/--'A'=---------------- ELEVA TION ANO DATUM ------------- DRILLER/COMPANY ___cR.;..;;u..:..:ss:..:..I_V--=a"'-lle=-<y=-W:..:..:e:.;.;II __________ _ DRILLING METHOD/FLUID _H--'o"'-1/o=-w=-S=-:t:..:ce_m_A..::.ug""'e=-r--------- DRILLING EQUIPMENT --'-F--=acc.ih~ng"--F--6=-------------- TOP OF CASING ELEVATION _13_8_.2_2 ________ _ GEOLOGIST _D_. _Ba_r_rie=--------CHECKED BY _J_. J_o_ne_s __ c f--a.. (1) w~ D 1- 2- 3- 4- 5- 6- 7- 8- 9- w >-_, er: a.. w :::;: > 4 0 Cf) u w er: wcr: _,w a.. CD :::;: :::;: 4::::> cnz 10- IX 77 BWBS02S01011.0 11-I IX 12- 13- 0 _, u i: a.. 4 er: Cf) Cf) 4 _, u _, 0 Cf) CL CL 7 0.0 :---- 7 15 1 ..•••...... I----<---· DESCRIPTION Asphalt at surface LEAN CLAY WITH SAND dark grayish brown IOYR4/2, moist, medium plasticity, probable fill (15% sand, 85% fines) OVERBANK/TERRACE DEPOSITS LEAN CLAY very dark grayish brown 10YR3/2, moist, very stiff, medium plasticity, contains very pale brown 10YR7 /3 silty stringers (10% sand, 90% fines) WELL DIAGRAM l"' ~ j I"-"' --"'--~ - c f--a.. (1) w~ D H 2 3 H 7 f----8 HO H1 H2 H3 14=-~ .. I'-~ --H4 I I OGDEN BORING LOG Page 2 of 4 ----- I CLIENT Chula Vista Industrial Realty, Inc. BORING NUMBER BS-MW02 PROJECT NAME/NUMBER Brandywine Dist. Ctr, NO. 510920144 COMPLETION DEPTH 56.5 ft. I a,.e I-UJ (!) (/) z u 0 (/) UJ >-UJ er: ::) <(-_J II _J er: _J UJ1--0 c... E u _J WELL 1--Cl.. QJ Cl.. UJ Cl.. CD u (/) a. :i: u DESCRIPTION Cl.. QJw2 ::::E > ::::E ::::E D a. DIAGRAM w2 <( 0 <( ::) ~ Cl.. ;::! I D (/) u (/) z 0 -~-<( D UJ _J er: 0 er: CD I (!) (/) I 15 0.0 5 I 16 6 I 17 LEAN CLAY WITH SAND brown 10YR4/3, 7 moist, medium plasticity (15% sand, 85% fines) I-- I 18 :::i 8a Cl: l') I 19 9 I 20 20 21 t.) 21 ::,. I Cl._ a q- l.u 22 :5 22 ~ I ~ (j 23 "' ~ 23 J I is f::; ::,. 24 ~ 24 I 25 0.0 LEAN CLAY WITH SAND brown 10YR4/3, 25 moist. medium plasticity (15% sand, 85% fines) I 26 26 I 27 ~ 27 28I28 'II, Abundant cobbles, slow difficult drilling CL from 28.5 to 33 feet bgs 29 29 I ------------------------------- 3030 ___ I I OGDEN -----BORING LOG Page 3 of 4 BORING NUMBER ___;B=-S=------.;-M....c,Wc...;_0.;:.._;'2=------------I CLIENT Chula. Vista Industrial Realty, Inc. PROJECT NAME/NUMBER. Brandywine Dist. Ctr, NO. 570920144 COMPLETION DEPTH 56.5 ft. I I I I I I I I I I I I I I I I I I I--a. (lJ w2 0 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 45-- w >- J a: a. w ::;: > t 0 Cf) u w a: wa:: JW a. CD ::;: ::;: t :::J en z I- z J 0 u 3: 0 CD w u «~ a. E Cf) a. 0 a. «- UI I en0en ..J ·« Iu .....) WELL 1--u DESCRIPTION a. (lJ I DIAGRAM w2a. .....) t 0 a: 0 en CL 31 32 33 ·. ·. ·. · SM SAN DIEGO FORMATION 34 Silty sand cuttings 35 36 C5 37Lu 5 V) Cl.. s,: c:i V) 38 ~ ~ ' ..... "' 0 "" -. J V) 390 0 0 Silty sand cuttings 2 3 4 5 6 I OGDEN -----BORING LOG Page 4 of 4 I CLIENT _C_h_ul_a_V_is_t_a_In_d_u_s_tr_ia_lR_e_a_lt_._y'-, _In_c_. -------BORING NUMBER _B_S_-M_W_0_2 _________ _ I I I I I I I I I I I I I I I I ___ _ I PROJECT NAME/NUMBER--Brandywine Dist. Ctr. NO. 570920144 COMPLETION DEPTH 56.5 ft.· 11 1--IJ.J (!) (/) z u 0 (/) IJ.J er. ...J I IJ.J er. => <t-·c:i: ... J ...JIJ.J 01---c... IJ.J c... CD c... E u ...Jc... a, u (/) a. u DESCRIPTION IJ.J~ :::;: > :::;: :::;: CJ a. I < t 0 <t => 3: c:i:-c... ...JCJ (f) u (f)Z 0 <t LU ...J l!l er. 0 er. CD I (!) (f) SM 47- 48- 49- 50- 51- 52- 53- 54- 55--88 BWBS02S02D56.0 12 SILTY SAND olive brown 2.5Y5/ 4, moist, X very dense, wet, micaceous, no to low - 25 ~ plasticity (70% sand, 30% fines) X 56-Color changes to dark gray 2.5Y4/1 X 32 BORING COMPLETED TO 56.5 FEET BGS 57-SET MONITORING WELL, GROUND WATER FIRST ENCOUNTERED AT 55' BGS, - GROUNDWATER AT 40.4' BGS AFTER 1 HOUR 40 MINUTES 58- 59- 60- 61- 62- I WELL 1---c... a, DIAGRAM IJ.J~ CJ I lJJ --.. ~7 -· 5 - 0.. -- f--48 ----,_ -- c:, - vl ---f-- c:, -~9i5 ·. f-- f-- c:i -f--· J_ -·f----- f-50 51 'I: f-52 f-53 f-54 l, f-55 56 57 f-58 f-59 60 61 f-62 I I I I I I I I I I I I I I I I I I OGDEN -----BORING LOG Page I of 5 CLIENT Chula Vista Industrial Realty, Inc. BORING NUMBER _B_S_-M_W_O_J _________ _ PROJECT NAME/NUMBER Brandywine Dist. Ctr, NO. 570920144 COMPLETION DEPTH _7_6_f_t. _____________ _ DATE/TIME ST ARTEO _0_2_-_18_-_96_/_12_15 _______ _ BOREHOLE DIAMETER _8_" ______________ _ DA TE/TIME FINISHED _0_2_-_18_-_96--'-/_14_3_0 __ ~-~--- COORDINA TES _N_/A-''-------------- ELEVATION ANO DATUM------------- DRILLER/COMPANY _R_us_s.c...!_V-'-a-'lle'-'-y_W_e_ll __________ _ DRILLING METHOD/FLUID _H_o_llo_w_S_t_e_m_A_ug"'"e_r ________ _ DRILLING EQUIPMENT _F_a_,Ji~ng.__F_-6 ___________ _ TOP OF CASING ELEVATION 155.16 I I--a.. (l) w2 0 1- 2- 3- 4- 5- 6- 7- 8- 9- w >--' er: a.. w ::;: > 0 fl u w er: wcr: _,w a.. CD f)Z 10~ I 11-IX IX 44 BWBS03S01010.5 10 0.0 17 17 12- 13- J 0 u I a.. er: J - fl fl u 0 fl SC GEOLOGIST D. Barrie DESCRIPTION Asphalt at surface ALLUVIUM/TERRACE DEPOSITS CLAYEY SAND light yellowish brown IOYRS/8, fine-grained, moist. micaceous, low plasticity (80% sand, 20% fines) LEAN CLAY WITH SAND light olive brown 2.5Y5/ 4, moist, hard, micaceous, medium plasticity (40% sand, 60% fines) ALLUVIUM/TERRACE DEPOSITS CHECKED BY _J._J_o_ne_s __ WELL DIAGRAM I I--a.. (l) w2 0 1-2 1-3 4 5 6 9 HO 11 12 H3 1----1--- 1414-- I I OGDEN BORING LOG Page 2 of 5 ----- I CLIENT Chula Vista Industrial Realty, Inc. BORING NUMBER 85-MWOJ PROJECT NAME/NUMBER Brandywine Dist. Ctr. NO. 570920144 COMPLETION DEPTH 76 ft. I a-'1 f-w (.!) enzu0en >-wo: _J I w 0: ::::> <(-"<( I f-- J ....JW 0 a.. E u _J WELL f--a.. (lJ a.. w a.. CD u en a. u DESCRIPTION a.. (lJ w2 ~ > ~~ 0 a. I DIAGRAM w2 <( 0 <( ::::> 3: a.. _J I 0 en u enz 0 <(-0 LU _J LC 0: 0 0: CD I (.!) en CL "' "" ....... "' ~ I -15-... 15r-SC I "' "" 16-"" ~ H6 I" I 17-1"'-~ H7 "" ~ I I"'-~ H818-i"\_ ~ i"' '"' ~ I 19-i"' ~ H9 I" ~ i"'-~ 20-CLAYEY SAND dark yellowish brown I" K ~20 I 0.0 I"" "' 10YR4/ 4, moist, low plasticity, sand is fine- to medium-grained (80% sand, 20% fines) I"" "' I" "" 21-(J I" "' '--21 °" I Cl.. "" "' c:, I' I" "' Lu 1---- i22-~ I" c:, '--22 c::i I"" "' 0:: I (J I"" "' (/) 23-"' I"" "' '--23 "" "' I "" "" "" "" '--2424-"" "' II" "' .... I 1"'-"" 25-"" "" ~25 I 26-"" "' -26 "" "" "" "" I "' fl"-'-- 2727-"' fl"- fl"- fl"-I", I 28-I"'-"" '--28 fl"-"" -~ "" 29-~ "' ~29 I "' "' fl"--I"'---------------- T~ ~ -------------... ----------------Jo-= ---------30 '--- I I OGDEN BORING LOG Page 3 of 5 I I I I I I I I I I I I I I I I I I CLIENT _C_h_ul_a_V_is_ta_Jn_d_u_st_r,_·a_lR_e_a_lt~y~, l_n_c_. ______ _ BORING NUMBER _B_S_-M_W-'-0..::._3 _________ _ PROJECT NAME/NUMBEFt Brandywine Dist. Ctr, NO. 510920144 COMPLETION DEPTH _1_6_f_t. ______________ _ f-w (!) enzu0en >-UJ a: _J I UJ a: ::> <(-,<( I f-- J _J UJ 0 o... E u _J WELL f-- 0... cu 0... UJ o... CD u en a. 'i u DESCRIPTION 0... cu UJ~ ::;: > ::;: ::;: 0 a. DIAGRAM UJ~ 0 <( 0 <( ::> ~ <(-0... _J 0enuenz0 <( UJ _J ~ a: 0 a: CD I (!) en SC CLAYEY SAND fine-to medium-grained, "' I"" 0.0 "' ~ - same as above .... 31-"' ~ >-31 "' "' "' "' -"' ~ 32-"' "' >-32 33-"' ~ ..... ,_33 "' "' :::, a ct: -(!) - 34-"' "' ,_34 "' ~ "' "' ~ 35-"' ~ . -35 I"" "' ~ 36-"' ~ -36 l) "' "' ::,. ~ ---~ - 0... ->-- a ><,c ><' 37-' I' ~ ')(' ,--37Lu ><,c : 5 ~ ')(' c:::i ~ -)', -~ ~ ><' l) ~ ><' 38-eOOBLY GBADED SAND rHil::l Sil I dark VJ ~ 0 ~ >-38 yellowish brown 10YR4/ 4, dry, fine-to (\j ~ 0 -.J 0 ~ medium-grained sand (90% sand, 10% fines} ~ 0 i=S -~ 0 ::,. 39-~ 0 <'. ,-39 ~ Lu x ><' .. ~ ><' 0 Y' - 4040-Abundant cobbles, difficult drilling, rig y 0.0 o-SC ><x 0 > 00 chatter, cobble fragments are ><x ~ 0 oc metavolcanic and granitic rock ~ - - 41->00 -41 0 ·oc J oo - 42- 0 oc f----42 >00 0 _ 0 C - 43- iOO ~ - 430oc '<{ VJ oo ~ '- 0 _ 0 C <\j ,,. 44-~ oo I -44 0 oc O 0 ->---- 0 · oc - 45--f-45 ·.- DOO -- 0 oc ---1------I- DOO ----·-------- 46-----------·-~----·--~ 1---.--:,.. -· --f----46 -- I OGDEN -----BORING LOG Page 4 of 5 CLIENT Chula Vista Industrial Realty, Inc. BORING NUMBER _B_S_-M__;_W....c...O....c...3 _________ _ I PROJECT NAME/NUMBER Brandywine Dist. Ctr, NO. 570920144 COMPLETION DEPTH _7-'-6_f-'-t. ______________ _ I I I I I I I I I I I I I I I I f--a.. Cl) w2 D 47 48 49 50 51 52 53 54 55 56 57 58 59 60 w a.. :::;: I! f-wz >-w er: u er: ::::> <C-_,w w a.. CD 0 a.. E u (/) a. > :::;: :::;: D a. 0 <[ ::::> ::;: u. (/) z 0 <[ w -' "lIJ er: CD I 0.0 0 u -' i u a.. ~ <[ er: 0 SC SC DESCRIPTION CLAYEY SAND dark yellowish brown IOYR4/4, moist, medium plasticity (80% sand, 20% tines) SAN DIEGO FORMATION Silty sand cuttings Silty sand cuttings I WELL f--a.. Cl) DIAGRAM w2 D 7 8 Lu 5 Cl < 0.. so: Cl (/) J C) ~ ii=l c:, c:i I OGDEN BORING LOG Page 5 of 5 ----- I CLIENT Chula Vista Industrial Realty, Inc. BORING NUMBER 85-MWOJ PROJECT NAME/NUMBER Brandywine Dist. Ctr, NO. 510920144 COMPLETION DEPTH 16 ft. I ;;'1 f-w CD U'Jzu0 .U'J >-wcr: ....JIwer: ::> <(-<( I f-- J ....JW 0 a.. E u ....J WELL f--a.. QJ a.. w a.. CD u U1 a. :i: u DESCRIPTION a.. QJw~ ::.: > ::.: ::.: 0-9-DIAGRAM w~ <( 0 <( ::> 3' a.. ....J I 0 U'J u U'JZ 0 -~ <( 0 0w ....J er: er: CD I CD U'J SC '-- I . '--63-'--~3 '-- 1 '--·. >--,_ I ·'--64->--1--64 : >-- I 65-10·0 15 SJLTY SAND olive brown 2.5Y4/4, moist, '¥---65Xdense, micaceous, sand is strong brown 25 7.5YR4/6, fine-grained, mottled, moist to I X wet (80% sand, 20% fines) 6666- I 40 I 67---67 I 68-~8 c:, < ' l: 69-(/) 1--69 ~ I '-"' -"" 70->-70 I 71-t-71 I 72--72 I 73-t-73 I 74-.._7 4 I 75-BWBS03S03D75.5 15 eQQBL Y GBADED SAND olive brown -75 2.5Y 4/ 4, wet, dense, micaceous (95% 27 sand, 5% fines) I 76--BORING COMPLETED TO 76 FEET BGS t-76 SET MONITORING WELL, GROUND WATER FIRST ENCOUNTERED AT 65' BGS, •- n77-GROUNDWATER AT 55.3' AFTER 53 I MINUTES 78= ---t-78 I · 1 I OGDEN BORING LOG Page I of 6 I C~E; :hu: Vi:a Industrial Realty, Inc. PROJECT NAME/NUMBER-Brandywine Dist. Ctr, NO. 570920144 BORING NUMBER _B_S_-_M_W_0_4 _________ _ COMPLETION DEPTH _8_8_.5_f_t. ______________ _ I I I I I I I I I I I I I I I I DA TE/TIME ST ART ED _0_2_-_ff_-9_8_/_0_84_5 _______ _ BOREHOLE DIAMETER _8_" ______________ _ DA TE/TIME FINISHED _0_2_-_ff_-9_8_/_13_0_0 _______ _ DRILLER/COMPANY _R_u_ss_/_Va_ll_e~y_W_e_ll ___________ _ COORDINATES _N_/_A~·--------------- ELEVATION AND DATUM-------------- DRILLING METHOD/FLUID _H_o_ll_o_w_S_te_m_A--'ug"--e_r _________ _ DRILLING EQUIPMENT _F_a_il_in=g_F_-_6 ____________ _ TOP OF CASING ELEVATION 173.59 e I-wzuwwa: :::, I _J a: _,w 0 < t- 1--a... w a... CD a... Ea... a, u en a. w1! :::;: > :::;: :::;: D a. <t 0 <t:::, 3: D en u enz 0 < t- w _J w a: CD I 2. 3 4 5 6 7 8 9 10 5 9 10 11 BWBS04S01D10.5 11 12 13 en0en _J < tu _J I u a... _J t 0a: en GEOLOGIST ----'D'--. _B_a_rr--'ie ______ _ DESCRIPTION Asphalt at surface SILTY SAND light olive brown 2.5Y5/6, moist, probable fill SILTY/CLAYEY SAND olive brown 2.5Y 4/ 4, moist, medium dense, contains scattered cobbles and gravels, granitic, poor recovery due to cobbles and gravels, insufficient material to collect sample, probable fill (trace gravel, 70% sand, 30% fines) CHECKED BY l) :,. Cl. Cl 1' Lu 5 c:i ~ l) J WELL DIAGRAM J. Jones i Cl Cl: I I--a... a, w1! D 2 3 7 14 I I OGDEN -----BORING LOG Page 2 of 6 I CLIENT ---=C.;...h.c...ul.;;..a _V....c.is.;:.;;ta'--l:.._n-'-d'-'us_;.tr-'ia'-I_R.;;...ea;:;...l'""'ty-'-, -'-In_c_. ______ _ BORING NUMBER _B_S_-M_W_0_4 _________ _ I I I I I I I I I I I I I I I I I PROJECT NAME/NUMBER Brandywine Dist Ctr NO 570920144 COMPLETION DEPTH 86 5 ft w (!) en0 >- wcr: z (.,) -' en I w er: ::::) <t-.<t -' _.w ... - CL w CL CD 0 CL E (.,) -' CL (1) (.,) en a. (.,) DESCRIPTIONw~ :::;: > :::;: :::;: 0 a. I <t 0 <t ::::) 3: CL -' 0 en (.,) enz 0 ..,:-tw -' .w er: 0 er: CD I (!) en o-s..c. oo SM - 0 0( I\ 15-22 20 0.0 SC SILTY SAND dark grayish brown 7.5Y 4/2, IX fine-grained, moist. medium dense. no to 20 low plasticity, insufficient recovery to sample, probable fill (trace gravel, 75% 16-sand, 25% fines) 17- 18- 19- 20- 21- 22- 23- Probable fill soils to approximately 25' bgs based on estimated height of fill slope 24-adjacent to boring location SC . ALLUVIUM/TERRACE DEPOSITS 25--33 25 0.0 IX SILTY SAND dark yellowish brown 10YR4/ 4, 40 moist, fine-grained, very dense 26- IX I BWBS04S01D26.5 50 27- 28- 29- 3G= ---~ ··-·----------..:::: 0.0 I WELL ... -CL (1) DIAGRAM w~ 0 1""-~ ~ H5 H6 ~ ~ H7 I"' "" I"' "" - I"' "" H8 "' "" ~ ~ .... ~ H9 20 ~ "' I"'-"' .... 21l.) ~ "' :,,. 0.. ~ ~ c:, .... ' 1" ~ f"'-Lu f... i : 5 c:, -22 C) ~ "' ct: l.) ~ ~ .... J) 23 ~ f"'- 24 "" "" "" ~' ~ "' ~ "' - 25 I"'-"" I"' "" -26 I"' "" ~ "" -~ "" - 27 ~ ~ ~ 28 f"'- f"'-.... 29 ~ ~ 30 -- I I OGDEN ------BORING LOG Page 3 of 6 I CUEN T ----=C:..:.hc::.u:.::la_V:..:.is::..:t:.::a-=lc..:n-=-du::..:s:..:.tr:..:.ia=-l....:.R.:..:e:.::a::..:lt"""'y,:....;l:..:.nc.:.c'-. --------BORING NUMBER _B_S_-M_W_0_4 _________ _ I I I I I I I I I I I I I I I I I PROJECT NAME/NUMBER Brandywine Dist. Ctr, NO. 570920144 COMPLETION DEPTH 86.5 ft. w >-I .....) a: 1--- CL (lJ CL w w2 ::;: > 0Denu w a: 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46----- wa: JW CL ll) en z I-w z u 0 CLE u en a. 3: ~ .9: : 3 -LU ll) I 0 u - I CL a: en en u 0 en SC DESCRIPTION SITLY SANO dark yellowish brown 10YR3/6, moist, same as above LEAN CLAY WITH SANO ANO GRAVEL dark yellowish brown 10YR4/ 4, moist, low plasticity, scattered gravels up to an inch in diameter, fine-grained sand (20% gravel, 15% sand, 65% fines) WELL DIAGRAM I 1--- CL <lJ w2 D 31 32 33 34 35 36 37 38 39 0 2 3 4 5 6 I OGDEN BORING LOG Page 4 of 6 ----- I CLIENT Chula Vista Industrial Realty, Inc. BORING NUMBER BS-MW04 PROJECT NAME/NUMBER. Brandywine Dist. Ctr, NO. 570920144 COMPLETION DEPTH 86.5 ft. I ~ I-w (!) (/) z u 0 (/) >- wa: -' I w a: ::) <(-.<( I I---' -'w 0 c... E u -' WELL I--Cl.. Cl) Cl.. w c... CD u (/) a. u DESCRIPTION Cl.. Cl) w~ ::::;: > ::::;: ::::;: 0 a. I DIAGRAM w~ <( 0 <( ::) :i:: Cl.. -' 0 (/) u (f)Z 0 <(-0 I w -' .LJ,J a: 0 a: CD I (!) (/) SM I"" "' ' I ~ ~ ~ f--4747-.... ~ .... ~ ~ I ~ "' 48-2.0 SILTY SAND dark yellowish brown 10YR4/ 4, ~ "' f--48 moist fine-grained (85% sand, 15% fines) ~ "' "' ~ I 49-"' f--49 "' "' "' "' "' "' f-50I50-~ "' - I~ "" "' "' I 51-"' "' -51 h ic:, It: l!) 52-1--52 I ~ ~ 53-(J "' "' r---{)3 ::,. I Q.. "' ~ c:, l" ~ ~ Lu 54-:5 ~ ~ f-54 Cl ~ ~ ~ I (J ~ ~ .... 55-"' l--55 ~ ~ I ~ "' -l5656-~ "' "" "' I "" "' 57-SILTY SAND same as above ,,,. ~ -l57 I y ~ 58-\. ~ f-58 '),,'),, \. y -.J I 59-~ ~ 1--59 ....... ~ ')') ~ + ....... ~ ')') ~ 60-~ '),, 1-60 I ~ 61-(/) H31 ~ I " "' '11, 1-62 -52-= '- I I OGDEN BORING LOG Page 5 of 6 I -----CLIENT Chula Vista Industrial Realty, Inc. BORING NUMBER BS-MW04 PROJECT NAME/NUMBER Brandywine Dist. Ctr, NO. 510920144 COMPLETION DEPTH 86.5 ft. I <>'! I-w (!) enzu0cn I w wo: :::> <t--' 0: -'w 0 < t I1--a... w a... CD a... E u -' WELL I--a... (lJ :::;: > :::;: :::;: u en a. :i: u DESCRIPTION a... (lJ w.2! 0 a. DIAGRAM w.2! <t 0 <t :::> 3' -~-a... -' I 0 en u enz 0 <t 0 w -' w 0: 0 0: CD I (!) en SM u I ~ Cl.. c:, 63 "I" 3l,J 5 I c:, 64 u VJ 4 "' I 65 40 75 2" Metavolcanic cobble-no soil recovered 5 I 66 6 I 67 1.0 7 68 ... 8 I .. SM SAN DIEGO FORMATION 69 9 I ~ <>: 70 SILTY SAND light olive brown 2.5Y 4/ 4, a:i tr) 709420 ~ I moist, very dense, mottled, fine-grained, ~ ' "' 28 light gray 2.5Y7 /1, iron oxide staining VJ "" 71 locally, micaceous (80% sand, 20% fines) ~ 40 Cl.. 71 c:, I 0.0 ~ .... c:, 72 vJ 72 c:, a I c:i 73 73 I 74 74 I 75 77 BWBS04S02D76.5 25 SILTY SAND olive brown 2.5Y 4/ 4 to brown 75 10YR5/3, moist to wet, fine-grained, very 35 dense, same as above (85% sand, 15% fines) I 76 45 76 I 77. 77 78 _L_ 78 I I OGDEN BORING LOG Page 6 of 6 BORING NUMBER _B_S_-_M_W....:_0_4 _________ _ I C~E; :hu= Vi:a Industrial Realty, Inc. PROJECT NAME/NUMBER-Brandywine Dist Ctr NO 570920144 COMPLETION DEPTH 86 5 ft I I I I I I I I I I I I I I I I I I I--ii. (lJ w.2: D 79- 80- 81- 82- 83- 84- 85- 86- 87- 88- 89- 90- 91- 92- 93- 94- w J ii. Cf) IX I IX I-w (!) Cf) z u 0 .Cfl >-w er: _J er: ::, <t-<{ _,w 0 ii. E u _Jwii. ro u Cf) a. :i: u > ::;: ::;: D a. 0 <{::, 3: ii. _J u CflZ 0 _- g;- w _J w er: 0 er: ro I (!) Cf) SM 88 BWBS04S03D86.0 25 35 1.0 50 I WELL 1-- DESCRIPTION ii. (lJ DIAGRAM w.2: D L-- L-- L--,__ L-- 79 ~ ,__ L-- L--. f--80 ~ L-- Lu ~ ~ -~ 2 '----- 810.. ~ Cl -<'. c::, ~ "<( ~ ~ (/) -.._ ~ ~ c:, '--" v=l ·. '--"' --82 '--"" ,__ c:, ~ ci L-- c::i ·.~ I--- 83 '--·-c.- Hl4L--·. ,__ eOOBLY GBADED SA~D ~III:! SILI dark -~ f--85 yellowish brown 10YR4/6, moist to wet, very dense (90% sand, 10% silt) .... f--86 BORING COMPLETED TO 86.5 FEET SGS .... f--87 SET MONITORING WELL, GROUND WATER '-- FIRST ENCOUNTERED AT 76.3' BGS Hl8 89 o I 2 3 4 I OGDEN BORING LOG Page I of 6 I -----CLIENT Chula Vista Industrial Realty, Inc. BORING NUMBER _B_S_-M_W_0_5 _________ _ I I I I I I I I I I I I I I I I I PROJECT NAME/NUMBER Brandywine Dist. Ctr, NO. 510920144 COMPLETION DEPTH _9_1_ft_. -------------- DATE/TIME STARTED _0_2_-_I0_-_96_/_0_91_0 _______ _ BOREHOLE DIAMETER _8_" ______________ _ DA TE/TIME F !NISHED -,--0_2_-l_l-_9_6_/ ____ ~-----DRILLER/COMPANY _R_us_s_!_V_a_lle_,_y_W_e_ll __________ _ COORD INA TES _N_!~A, _____________ _ DRILLING METHOD/FLUID _H_o_llo_w_S_t_em_A~ug"--e_r ________ _ ELEVATION AND DATUM-------------DRILLING EQUIPMENT _F_a_ilin~g~F_-_6 ___________ _ TOP OF CASING ELEVATION _11_5_.8_5 ________ _ GEOLOGIST _D_._Ba_r_rie ____ ~-CHECKED BY J. Jones I-w t'J (J) z u 0 (J) wa: ...JIwa: ::::, <(-<( I I--... J ...JW 0 a.. E u ...J WELL I--a.. Cl) a.. w a.. Cl] u (J) a. :i: u DESCRIPTION a.. Cl) w1! ::;: > ::;: ::;: 0 a. DIAGRAM w1! <( 0 <( ::::, 3C a.. ~ D (J) u (J) z 0 <(-D w ...J w a: 0 a: Cl] I t'J (J) - Asphalt at surface 1:\ I"' I - SM ,__ SAN DIEGO FORMATION ~ >- I"'- H1-Silty sand cuttings I"' f"" f"" >- I'-f"" 2-!"'-f"" -2 f"" I"'-f"" >- 3-I"'-f"" -...._3 I"' "" - I"' f"" >- I"'-~ f-44-4" cobble noted in cuttings I"'-I'- I"'-~ >- I"- 5-I"' ~ I"' - I"' f"" 6-t.J I"'-I'-H3 ::,. I"'-I'-ll.. c:, I"'-I'-'I" Lu 1"'-I'-,_ 7-:5 f"" "' c:, -7 c::i a: l!) t.J V) 8-.. <"\J "" "" f-B 9-"' "" H3 "' "' ~ "' >- 10-~ "" -1061BWBS05S01010.0 15 0.0 SILIY SAt:,jD light olive brown 2.5Y5/6, ~ ~ X moist, locally mottled gray (80% sand, 20% ~ ~ - fines) X 30 f"" 11- I 30 "' ~ HI 12-I"' "" H2 ~ "" -~ "' >- 13-~ "" H3 "" i"" K -K -------· ----- 14-~ l's. I'-. ---14 -- I OGDEN -----BORING LOG Page 2 of 6 I CLIENT Chula Vista Industrial Realty, Inc. PROJECT NAME/NUMBER-Brandywine Dist Ctr NO 510920144 BORING NUMBER _B_S_-M_W_0_5 _________ _ COMPLETION DEPTH 91ft I ,ti! t-w (!) [/] z u 0 [/] w >-wa: => <[-_J <( II _J a: ....JW t--0 CL E u _J WELL t--CL Cl) CL w CL CD u [/] Q_ :i: u DESCRIPTION CL Cl) wJ! :::;: > :::;: :::;: D a_ DIAGRAM wJ! D <[ 0 <[ => 3: <[-CL ~ D I [/ J u UJZ 0 <[ w _J l.O a: 0 a: CD I (!) [/J SM 1"'-"" I -1"'-"" '- I"'-"" 15-I"'-~ .H5 I ~ ~ 16-~ ~ H6 ~ ~ I 17-"' "" H7 "' "" "' "" - I " "" 18-~ ~ HS 19-~ "" H9I ~ "" -~ i"'-'- 20-Silty sand cuttings 1"--~ 'e---20 I ~ "" ~ "" '- 21-l.l 21 ::,. I Cl.. a l' I"--Lu I"--:::) 22-:5 a ~22 c:, Ct: I -(j ~ ~ (/) 23-"' ~23 '"' ~ I -'"" "" '-2424-~ "" -~ "" '- I ~ "" 25-SILTY SANO cuttings slightly darker than ~ "--25 above "" ~ -"' i"'- I 26-"" "" -26 I "" ~ >-2727-"" "' -~ i's '-~ "" I 28-~ i's >-28 i"'-~ "" 29-~ "" ~29 I ~ "" ~ "" ---··------------·------K--K---- 30 "Jo-~ ---. -· ------'---77 BWBS05S02031.5 20 1.0 I I I I I I I I I I I I I I I I I I I I OGDEN -----BORING LOG Page 3 of 6 CLIENT Chula Vista Industrial Realty, Inc. BORING NUMBER _B_S_-M_W_0_5 _________ _ PROJECT NAME/NUMBER Brandywine Dist Ctr NO 570920144 COMPLETION DEPTH 91ft i>,!! I-LU (!) (J) 0 >- LU 0: z u _J .rJJ I LU 0: ::::> <t-<t I1--_J -' LU 0 c... E u _J WELL I--Cl.. (lJ c..: LU c... CD u Cf) a. -u DESCRIPTION Cl.. (lJw1' L > LL 0 a. I DIAGRAM w1' <t 0 <t ::::> 3: Cl.. _J0 (J) u rJlZ 0 -~-<t 0w _J LU a: 0 0: CD I (!) (J) SM SILTY SAND light yellowish brown 2.5Y6/3, I"" ~ 30 moist, very dense, fine-grained, locally I"" IX iron-oxide stained (85% sand, 15% fines) I"" 31- Ix 50 1""-"' '-31 1""-"' - 1""-"' 32-I"-"' -32 1""-"' "' \ >- 33-"' -33 "' "" ~ "" >- 34-"' "" -34 35-~ I"---35 I", ~ 36-~ "' '-36 ~ I"\ I"-- 3737-l.) ~ ~ ::,. Q.. ~ 0 >-" I" ~ "' Lu f-- I"-"' :::, 38-:5 0 ~38 c::i ~ "' ct: l.) I"-I"-VJ I"-K39-"' -39 1"'- I"- I"- II"- I"-- 4040-Silty sand cuttings, same as above I"- I"-I -I"-I"- 41-"" I"-f-41 I"' I"- I"-1"' ~ 42-I"-I"-f-42I"-"' I"-"' ~ I"- f-4343-~ "' ~ "' "' 44-"" "' f-44 45-~ SILTY SAND same as above with less iron-"' f-45100BWBS05S03046.0 35 ~ ~ ) oxide staining, (85% sand, 15% silt) 46·=·1 50 -·· ------G __ ~ --------------· ------ 1"' "' ---· ·--· -· -----~--------------------.. ---- f-46 ---'-- I OGDEN BORING LOG Page 4 of 6 ----- I CLIENT Chula Vista Industrial Realty, Inc. BORING NUMBER BS-MW05 PROJECT NAME/NUMBER Brandywine Dist. Ctr, NO. 510920144 COMPLETION DEPTH 91ft I ~ I-w (.!) enzu0enwa: ....JIwa: ::, <t~ .<[ I ....J ....JW I--Cl... w a... CD 0 a... E u ....J WELL 1--Cl... a, u en a. :i: u DESCRIPTION Cl... a, w1! ::;: > ::;: ::;: 0 Q. DIAGRAM w1! <[ 0 <[::, :;: Cl... ....J0enuenz0 <[-0 I w ....J .UJ a: 0 a: CD I (.!) en SM I" ~ ' I - l's, 47- l's, ~ f--47l's, ~ l's, "' - I "' "' 48-I"' ~ f--48 I"' ~ i"" "" -I 49-"" "" f--49 f----50I50-", "" - I"" "" - I"" "" I 51-I"" "" -f----51 . ·' I"" "" .... I"" "' -~ - I"" "' a: 52-C!) f----52 I l's, ~ I"' ~ 53-Silty sand cuttings, same as above l.) I"' "" f----53 ,,. I CL. I"" ~ c:, -' l' I"" ~ Lu 54-:5 l's, ~ f----54 Cl l's, "' ~ I -l.) "' "' -.. ( JJ 55-"' I"' ~ f----55 l's, ~ I "" "" f----5656-"" "" -"" "" .... I "" "" 57-I"" "" -57 I'-'\, -~ y" ->'>< y II .)' '><.,,, 5858-)'>< y y 3 )I" '><.,,, n:' )'>< '))I. c:, I 59-.;, ),.';,. ES f----59 -) '))I. ,,. y ),.';,. < i ')") Lu - y ),),. l60-0.0 SITLY SAND olive brown 2.5Y4/4, moist, >) )') f-60 I y )),. very dense, no odor, darker color than .,,,> ~ - above, slightly more moist, water droplets lo.a - in headspace bag (85% sand, 15% fines) Cl < H3161-<,: I ~ -' ----·-,-"' --------------------------,,.---:- f-62 -----52------------~ -'- I I OGDEN BORING LOG Page 5 of 6 ----- I CLIENT Chula Vista Industrial Realty, Inc. BORING NUMBER BS-MW05 PROJECT NAME/NUMBER Brandywine Dist. Ctr, NO. 570920144 COMPLETION DEPTH 91 ft. I ~ f-w (!) CJ) z u 0 CJ) >-w er: ....J I w er: ::) <C-'<[ I f--.... J ....JW 0 a.. E u ....J WELL f--a.. QJ a.. w a.. (D u CJ) a. u DESCRIPTION a.. QJ w 2:' ::!: > ::!: ::!: 0 a. I DIAGRAM w2 <[ 0 <[ ::) 3: a.. ....J I 0 CJ) u CJJZ 0 <[-0 w ....J 'l!I er: 0 er: (D I (!) CJ) SM l) I :,,. 0... c::, 63 " L.J s Cl I ~ l) 64 {/) I 65 5 I 66 I 67 7 I 68 8 69 g I ~ 70 SILTY SAND same as above but slightly ~ {/) 700.0 ~ higher percent of fines (80% sand, 20% L.J ' I 5 "' fines) {/) "" 71 ~ 710... Cl I ~ f.- c::, 72 (ij 72 c::, c3 c:i I 73 73 I 74 74 I 75 SILIY SANDLCLAYEY SAND olive brown 75 2.5Y 4/3, moist, very dense, cuttings have 1/2" to 1" balls, (80% sand, 20% fines) I 76 76 I 77 77 rn---78 I I OGDEN BORING LOG Page 6 of 6 ----- I CLIENT Chula Vista Industrial Realty, Inc. BORING NUMBER 85-MWOS PROJECT NAME/NUMBER Brandywine Dist. Ctr, NO. 570920144 COMPLETION DEPTH 91 ft. I a'1 I-w (!J Cf) z u 0 Cf) I w wa:: ::i 4-_ J 4 _J a: _,w 0 I1--"-w "-CD "-E u ._, WELL 1--"-Cl.) ·:E > :;: :;: u Cf) a. '.I u DESCRIPTION "-Cl.) w~ 0 a. DIAGRAM w~ 0 4 0 4::l 3: 4-"-_J Cf) u cnz 0 4 0 I w _J w a: 0 a: CD ':I: (!J Cf) SM I 79 79 I 80 ~ 5 I l.) 81 ::,. 0.. C) C) I 82 0.0 LEAN CLAY WITH SAND dark grayish brown vl CL 2.5Y 4/2, moist, driller reports drilling ~ C) slightly different, low to medium plasticity, ci 83 fine-grained sand (15% sand, 85% fines) I 84 ~ I "< (/) 85 "' BWBS05S04D85.5 25 0.0 EOOBLY GBADED SAND WIIH SILI olive % I brown 2.5Y 4/3, wet, very dense, fine-to 50 medium-grained, micaceous, free water in sample, (sampler dripping) (90% sand, 10% fines) I 87 I 88 I 89 I 90 75 40 SILIY SAND very dark gray 2.5Y 3/1, very dense. slightly organic odor, moist to wet BWBS05S05D91.0 75 (75% sand, 25% fines) 91 BORING COMPLETED TO 91 FEET BGS I SET MONITORING WELL, GROUND WATER 92 FIRST ENCOUNTERED AT 76.5' BGS, GROUNDWATER AT 74.5' BGS 40 MINUTES 2 I LATER 93 3 I -------·------ 94_ --------·-4 --------- I I I I I I I I I I I I I I I I I I I I ULS REPORT FEB-03-96 03:03 PM ULS.SERVICES.co 619 439 8398 P.01 I I I I II I I I I I I I I I I I I I FACSIMILE TOTAL NUMBER OF PAGES !5r /nc!t1"'Jlve ) DATE c)-::: ~ -q ~ , TO FACSIMILE NUMBER t../ 5 S -{f/9~3 ATTENTION UCl1 13a,-r1 e COMPANY C)f;.{)EA/ ADDRESS CITY, STATE, ZIP .c':. i...._)Ct. i l l);E'/jO FRO.U " W.-!!'::% ULS SERVICES COMPANY P.O. Box 724 ~---·. ,"'' .......... ::; 242W. Lewis - ULS SERVICES COMPANY Pocatello, ID 83204-<>724 ioe:.,; :,~ ~•-·:tt 'r:i ~·-.•!#!,•,··•· v, -:)1", ... ;::.r :·;·re• ·; (800) 528-8208 (208) 234-1441 - TELEPHONE 800-528-8206 Please call (800) 528-8206 if you have difficulty reading this document. COMMENTS: T.)Q,1 -&/Jc,j ((,/Cri.~ f;",~;-~t fc·c/a<./ r; GTE.· This document is conjidentia/ and ifyou are nor the intended recipient. disclosure. cop.ving. or distribution cf this information is prohibited. Please notify us at the number shown abo,·e so that we may retrif!i·e the Jocummt at nu c:o:,t tu yuu. Thank you, UL$ Services Company I I I I I I I I I I I I I I I I I I ULS SERVICES COMPANY SpecialiZed S11,im tcr En,ironme11t1I and Constmtion E119inetring WORK ORDER AGREEMENT JOB SITE LOCATION: JOB P.O. No.: lwf'/C t~7C l3n·ui.·/v1,.1,,1~ CllY: STATE: C /-1 ldc, t./: ~ fr:1 Ca PHONE: BOOK/PAGE-ZONE: SITE CONTACT. JOB DATE: WORK REQUESTED: (SCOPE OF WORK) ORDER DATE: CLIENT: BILLING ADDRESS: 775 Yellowstone .Avenue Pocatello. ldano 83201 800) 528 8206 5580 La Jolla Boulevard La Jolla, California 92037,7651 619) 459-8598 ORDERED BY: Den &-:\rv-c c·. 5.'S/0 f11ore /,1t.)l-1 1 ;c!. Dr, CITY, STATE, ZIP: V 1r-1q ·· 'l-5B -fti'-f'/ PHONE: fl,(1-45f', ·-c-r.-,43 WORK PERFORMED: TRAVEL HOURS 1--------------1 ·; f; f:M P.C:..L Cc,,'\l1uL.tive. (Jt-, L+y Su..rl/t!''( LABOR HOURS ~ .o DOWN HOURS A~·,\, .::!..c"1 pC'\ '!;>::,1ve. I~ rc.·L·"-V\c\ ·, ~tc.h{c+ i c,'\ _ c-.u\....-\ cc-1\(\c:'c-t ·,cv\. 1\.tcde·~-L.L_-;c,\+~c·l L{+1 [·, ~ ,~s ""'c<~·lc'.eA LU' i C, pIv\ l'... p,, ·, ~ \~ eJ (t•'V' OL0 ~ ·, 1,tc(1 c,·,4 I" \,.-J ol. I {ec~ i CV\ I Apr~·.:.-:')( IO' >' (Q, Llt vey z,.:"°'\.'\f' CJ.vC<.t.'-',J ... ?Cl.C (1 po1v\-l-pc111,d ec<. (1...,,.J l\ pi v\ k_ l,c.)( E ~ { r:;:,~ a ) , *. E: N'I ..CM D .:!~r1 t:k,c. ·{ 'i II e -StH \.' ~ y ~er· a.,, 'I t....._ e t·a l wtc.-t-:, ".;7 C'l.·""'C' ~ .. 1.0 I I c-5 t4l1Tlc'N '. s(!~h,c t,-~l("L..\c+-l~e C\.\.i\,c\ V\C'I.'\ -CC'l.\C\1..tc::-l:v.(' qt;!, ii c_.-; y,,,ci.y c r M""Y ~"·-1 be lccn·L,·cl due k.· u~1La~t{11r((c~ c(,-c.tti~\~tc ... qcc~ ; e. r~ .. ,lo"d~~l+' "Pvc_ p,p~, ,·e.i~\t"•iU~ C<""~,.,~c:,e+c.)_ 5-f~c:.."l,'\,.:lr -6uc_:r]:J+ t"~l'C-tL,~4,i.-tc·~ C\ll ~c~~1lJl-c: ~c1._tn:ec,.f 11..,tc, 1 , e (o!.> bc..l,h~, l\'J1~JD,.Jli"1~ t; h'. SIGNATURE OF ULS REPRESENTATIVE DATE cJ -5 -·q <+,. NOTE: THE WORK PERFORMED ABOVE IS PERFORMED TO INDUSTRY STANDARDS (OR HIGHER); HOWEVER, IT IS THE RESPONSIBILITY OF THE CLIENT OR EXCAVATOR TO CONTACT,ALL UNDERGROUND FACILITY OWNERS AND TO DETERMINE THE EXACT LOCATION OF UNDERGROUND FACILITIES BEFORE EXCAVATING. EXCAVATION WORK NEAR UNDERGROUND FACILITIES MAY RESULT IN INJURY TO PERSONS OR DAMAGE TO FACILITIES. THE CLIENT OR EXCAVATOR WILL TAKE ALL STEPS NECESSARY TO AVOID CONTACT WITH UNDERGROUND FACILITIES. STATE LAW MAY. REQUIRE THAT HAND TOOLS BE USED TO UNCOVER FACILITIES WHEN WORKING WITHIN 2 FEET OF EITHER SIDE OF FACILITY. LAW MAY VARY. ULS AND ITS REPRESENTATIVES ARE NOT RESPONSIBLE FOR INJURY TO PERSONS OR DAMAGE TO FACILITIES. CLIENT'S SIGNATURE BELOW IS ACCEPTANCE OF RESPONSIBILITY AND ACKNOWLEDGMENT OF SATISFACTORY COMPLETION OF WORK PERFORMED ABOVE. THIS DOCUMENT WILL ALSO BE FAXED TO CLIENT FOR ACKNOWLEDGMENT OF ABOVE. ULS SERVICES COMPANY Michael W Benedict or Steve Wilkir.s CLIENT TELEPHONED DATE• I I I I I I I I I I I I I I I I I I I 5:05 PM ULS.SERVICES.CO 619 459 8598 maMD StJRV'n' Sn'!: nn'ORMA'M:OW ARD CALIDRA'l"IOR SUIT Client: QC,QCN Project Naaea 1-t:·1c -t-10-ro -S,.--c'-""d';f::v.·,~u2 Date: ~ -· 6-Cl(e Surveyor Naae: ,h h ,,-i:, l?ei ,'rr ek--, .. --..... Unit Model Naae: TW-6 or~ini 3 Serial NO-: · SUrvey scope(ie.ost, Debris): /L1,1 /rlEtcf ;Yb;1 c1-i-1c"'11'/ic~ construction Mediua(Reference if 7len.own, ie Steel, fiberglas) Calibration(Site Specific EK Signal Roise Adjustment) Instrument Highth(ft): _____________ __ senaitiTity Setting , __ _..._ _______ __ Ground surf'ace Type: <t ;5 /)/le? /{-) SORYE! DA'l'A Trial 1 Bighth • . Setting . . Trial 2 Bighth : I Setting . . S11rface Ke~al Interference1~-----/-l~?'YJ •. _1_e.··----------- Otilit:, INterference =-----..i1~1~??--1.;;;.e-~------------- Anomaly Sbape(Surface Projection): ____ .,_1.,_:~~'~-e_, _______ ....;._~ Diaensions: ___________________ __,, ___ ___ N'earest Reference Point ( ie. Bldg.): ________________ _ I..... /. ' ) I /,. . t I ;L- UST Inside Tank Measurements UST 1 B = --,,,..r T = ~-----;> J.a =---- tJST 2 ULS SERVICES COMPANY t l ~ (<'. ./ OST 3 P.03 I I ELECTROl\lAGNETIC PIPE AND CABLE LOCATION EMPCL) QA/QC SITE SHEET I Client: OG.D ~ N Project:\fame i<c''{C,-..f IG7D Br,,.'VIL"lyw1"1e I Dnte: &..-5· -<=1 ff.. SurveyorName: (>41,-(j Kei~"tle( Unit Model Same RD 400 Receiver & RD400 Standard or HPTX High Watt TransmitterISerialNos: Receiver ____ _ I METHODTO PERFOR;\I Trans ------ Specific Comments and Limitations I PASSIVE ,\IODE 50/60 hertz (power) I Radio ( VLF) 8 and 33 khertz) GROU'.'iD l~DGCTIO~ MODE I Spread 33 khertz lnline Specific Lines T 's or Branche~ "" I Parallel Lines(closely spaced) SITE \'1Sl'AL INSPECTIO'.'i of CTILITIES and CONNECTION MODE Propane AST . 1e OJ,. e,·v e,, I Natural Gas ~1eter {'7)'1.t? OI-J~t.',·1.:€?C:, Electric ~leter 1',:cp·,;: c,-,,,, e,,·t /11 l<J C'; I I Telephone/Cable T\' CJ L_T] (~I\J _fi__ I JJ tc1 C :._ r u '{ fo-: CunJuits /1/('>te CLJ-;, .. ~-:* ,,t:·A foe! Lines IV'-""l1e C /.J-5 e,·.J;ci Water \!Jin.'Well Pump Domestic Fire Hydrants /\20,· 11 ltc.1C I I Fire Sprinklers /\·::--.1 e c b; c:·, .., ~c ( rrrigation C,rt1l1cv1 to .P{c: 1r-/inal,(.~, Light Poles ;Vk,,..1 e -oh~ (:t'v e cl J I MANHOLE LID Ll\JSPECTI0:\1 for UTILIIT TREND DIRECTION Sewer and Clean-out ,, ').. t:. :ii Storm Drain (or inlet) /~,,,:, -:,h·,. c-:rv v c,- 1 Electric /t/.:-vl e:~· r-u") e:,,-v e c. Telephone 11/zvz c". C~"U7e~,/o/ rel FIBER OPTIC CABLES?? t-tA' ,k'.'..A/Ct-d Iv' I PLASTIC wATER PIPES?? ll 11./ k...1\,'C t<J XI OVERHEAD LINES [N A.REA"" ~2:> A' D 6'-?::::::-. Surveyor Initial g lE L'f:_ LA- lf.._ L.1:_ 1:!:::._ 1.!f_ 1£:... j}L id:_ lZ.. a_ t/l J&_ L _ a_ See Pg. 2 I. Ground to Earth Conditions" Soil -~ois~_o1r Dry/concrete/cdood Poor? Review of Utility Drawings and Client Review" -,;;,--__ JiOTE:Jf_in.dicated_a(ter_Suoi_ey.or_lnitiaL(_*..!)_please_r.efcr_to_page_l_for_additionaLComments an_d __ Li111 i.t:1ti~_n_s_ __ ~ I I I d5:06 PM ULS.SERVICES.CO 619 459 9598 EMPCL QA/QC SITE SHEET SPECIFIC COMMENTS • LIMITATIONS page_ I 1ient: Ct.,.Dr:tJ Project Name: 11:11C·-4 /k,(O 'f.m .. v"ldyL.J/v,e Date: ;J.--""i·-crt, I Sun·eyorName: · C tl (·,,., ~~ c 7 ' 1 ,v,€··( I fc c I .-V\. 1. ( ,. l ( .. . J o (,0 fer I. t'.: I1" . k • J P.a5 I _____ ,· __ ~1 .... rr ... ··, L..;,·1""'"r;..:.;:l_.l_ .... j-j_,j. v'---ea...:-vt~c;...;:·,I'""'-;, ... · __ AJ......;:;1_/-""'2 ________________ ,. ____ _ 1.::ki,,...·'_-...1(........L, )(..:..1;/ul.;:.:A:...,;+_··.:....:rc:::;.'M--l....--!../....1-'c-,..:.., ..L..L_ ..... -)~· ~:.;.;.-:.?--1,l::.:,·'I...:....:) e::=!..:.~--L../1..:..::i.;...7_· ~c-'~~{-".._);f.....:(....:t:....:.1.:a...('):.l::,l,:.:;_C.:_...IOc..." -..1..o~I,) ~:::::,::...:...e ~...:..' -~\/_;(_' ~;__;_ ___ _ t'll7(~ t1 Ac! cc; ) ;,,1 15 ,.cu-1rll// ;C,Ji l~'-C. t. ~ 1,,1 o I; ic _,., : 1 /__., (. >- C. f / - l _______ ___;v::...';..a..1~~~c;...:..i1cr.;..;.··,.1..(~l-.. · 1 t_..,'C...;..;~t::......1..i..;;e1~/------------------------------,--------~- I----,-------------- I 1------------- 1 1 ___________ _ 1------------ I --------------------------------------- 1 -~------------------------ I ULS SERVICES COMPANY ----·-.... ___ __,_ I I I I I I I I I I I I I I I I I I I WELL DEVELOPMENT AND GROUND-WATER SAMPLING LOGS I OGDEN WELL p~;~ . I/wine iv,U;¢>t- I I I I I I I I I I I I I I I I I DEVELOPMENT JOBNO. SITE PREPARED BY.JC- METHOD: OVERPUMPAGE .. INmAL WATER LEVEL 5 :2 · 3 / h,s REMARKS: BAILER v RNAL WATER LEVEL SURGE CAPACITY OF CASING VOLUME BETWEEN CASING AND HOLE (GALLONS / LINEAR FOOD BLOCK (GALL~FOOT) (ASSUMING 40% POROSITY) z~::::::~~ . -AIR LIFT 4" • 0.65 1.47 4" CASING AND 10" HOLE: 1.37 OTHER 4" CASING AND 12" HOLE: 2.09 HOLE DIAMETER dh .. ~ --1 d w ~OUN) WELL VOLUME CALCULATION: 30 ~(_"'!j-of ~VJ WELL CASING SURFACE _...,. r CASING VOLUME= Vc=11"(¥)2 (To-H)=3.14 (-2-)2 ( INSIDE DIAMETER dwlDa __ -) = OUTSIDE DIAMETER dw OD : ~ FILTER PACK [(dht (dw00J2} *)( ) -~ DEPTH TO: H • tQ.3~ PORE VOLUME = Vt u 2 --r-TD-(SorH) P = WATER LEVEL (* if S>H uses, itS<H useH.) TD BASE OF SEAL 1 ) 11}-3.14((-2-t-(-2-t] ( )( -)= BASE OF WELL IH!UVAI. TOTAL WELL VOLUME =VT= Vt +Ve= + = __ ft.3x7.48 = __ gal. EST. FILTER PACK --I dhl-POROSITY p = DEVELOPMENT LOG: CUMULATIVE COMMENTS: -WATER QUALITY R.OW WATER DATE TIME METHOD aAPSED RATE REMOVED BEGIN/END TIME (gpm) GALLONS pi CONDUCTIVITY TURBIDITY TEMP. - 12·M-1c.;. /&,OD ba;lev 0 i-,.,J ~~ /" r.6 t;, lS~ Vf!vLA Jtf g (BEGIN) /71•1'1 :, . 5 2-~ S.8& c;-.'13 )I ~, JI,;,/() /{p 3D t;.13 q.o3 ,..-iJ1vi,.;.-i 1~3 l~t:5' 15 3.s .;.1s '1.0~ V?-~ fv,;D U> 2,~ ~.'ll ~.11-~,, / l!J.t ~fl ... ~c.. .. ~·~ b-r JO NI'""' tp52 52-31" ', ."l'f "I. 'g 1 1,-r.t; h5S ~5 t/-0 .:;. l'g r;_qg 1,g.y 17()¢ ldtD '/5 ~.'id &,. 22 ~/. "1 , v 11¢3 1 I' 3 , v tt<l> C:,.~ &,.¢1 ~1./6 n@s i ~5 iJ 5D ~.11 5/12 V/ u./> at l3oD Ott 2-11-j {p -0d v,Dt b<!s )t1 z.o ~lloYL()f.J~d>'ncJd >:rc-n fem~- I OGDEN WELL PROJECT WELLNO. 11/J lu'-{) Z- I I I I I I I I I I I I I I I I I I DEVELOPMENT JOBNO. l~~/il'Wl/u _.1,,t ~- PREPARED BY METHOD: INmAL WATER LEVEL 3 0 S--. , ~ R~ • J-OVERPUMPAGE . . ~ . f) u~? ~~s~_<J!&-1cl .~ ~ +Jh i/ FINAL WATER LEVEL L/ 2, -.: //~<:, ~ BAILER rf J .drrl 1,1-1ork SD tlz.U /ev't!I t:; f'dlec/;~8 t;._ ,I; ) J<'.x, CAPACITY OF CASING VOLUME BETWEEN CASING AND HOLE (GALLONS / LINEAR roon JL..y SURGE 1 BLOC~ ( GAUONS / LINEAR Foon (ASSUMING 40% POROSITY) JJJ'f-' , 2" · 0.16 2" CASING AND 6" HOLE : 0.52 ' "~ , . - 4" • 0.65AIRLI 2" CASING AND 8" HOLE : 0.98 J. 6" • 1.47 4" CASING AND 10'' HOLE = 1.37 OTHER 4" CASING AND 12'' HOLE= 2.09 HOLE DIAMETER dh = 2-/t' --i d W14-;0UICI WELL VOLUME CALCULATION: WELL CASING _..,. SURFACE INSIDE DIAMETER dw ID= __ ! 1 CASING VOLUME =Vc=ir(dwJ 0 )2 ( ro-H)=3.14(-2-t( -) = OUTSIDE DIAMETER dw OD = -. J S FILTER PACK [(!!b.J2 (dw00J2} *) ) . I D£PTII TO, rJ )( ;;f ) -:l PORE VOLUME =V,=ir 2 --r TD-(SorH) (P = ( t1~W7& ;: t./-12. )",,j)J 0~ WATER LEVEL H : ,._· _,u ltJ/:J,/YJ~ (;tS>Huse~,;fS<Hu:H.) f, /./r ,-' (1. ?C'ect Ir-TD BASE OF SEAL :::~ 11}---~£e:. 3.14[(-) -(-)]( -)( )= J BASE OF WELL -s.~t 1l 2 -2 · '-( ) 2.. INTERVAL _':, ~ ~c vt4 ?. Vv'f. .J/c-r . ('1. ~ -• EST. FILTER PACK p = --l dh I- TOTAL WEL cii:. ~ .fk~ Ve~ + ~ ft.3x 7.48 ~::... gal. POROSITY " Bf t,vrf./hat,/c' ~-a DEVELOPMENT LOG: CUMULATIVE WATER QUALITY COMMENTS: - FLOW WATER REMOVED DATE TIME METHOD ELAPSED , RATE BEGINiEND TIME ., GALLONS pl CONDUCTIVITY · TURBIDITY TEMP. 2 ~/1-'j/. 1 :Llr /_'l:;;, I 0 -?. / s-6t-f Z3'-IE3 v~rv 1-"7 ? (BEGIN) · /1.Jll!v d,'v .) . ..) I (3 (( (0 v;.1z !,S''J G :3 i( /2.L flt2.. ( ( 11*1-( ( /g-l·k (.JQE,3 // ?f\ 2 '1 II .,, si I I 2-c) I ~ ;-.~ O :2-/1£ 3 / I bf Ci 11()$1-52 · ({ -6-Jf" ,J. 70{:3 '1-(). t {( (i Z.> ,, I I It) ':)"7 i( ~r LI 252 ~-Zf 3.o U:> I( ?tf.'f L'' ( If ( °O ii i5 •( 3S-~;-Zo 3.o3E3 Ir 7o.1' l\ /ri.tf c( 1q7-·· ,c !J(7 ~.tt 3.20£-; ( \ 156 12cr< (( /2.~ I l t-f.« t:,.(f 3s-o~ ~ ii 1~-1 /1,t,1,1/'-L-1 L<rvi!~ l ( I.S~ w, 172 o t ( /l/6 I ( 1'-lffeJc. /i.>:r 5-1>1£3 (( 15'-0 u /zZ.I If 11 I I( ti 1-6t"'l 3.3oF 3 ((; 15--1 122 if-I( H'f ' ( 'k / ct; ;,. ,,.,?·f:s ,). " u . ~c<1~J 122 i 22.-;-( t..f S-. .!. '1 ?(,,7 '32SE3 I 11)1' fl .f 122-::/· ,I I 'f 7-/( .. -.-~ .i;-o_ fl)) 3-'21£] 10.g ijj I OGDEN WELL PR~JECT M WELLNO. l'i ,.J ,~ jj.Nfl rv,1,u-¢.5 I I I I I I I I I I I I I I I I I DEVELOPMENT JOBNO. I SITE PREPARED BY ~ c. METHOD: OVERPUMPAGE INmAL WATER LEVEL L/& · V P5..S REMARKS: 1eVt!.I 1akn <!!. /:3D3 .:r.., ,tid I H.1-D BAILER v FINAL WATER LEVEL SURGE CAPACITY OF CASING VOLUME BETWEEN CASING AND HOLE (GALLONS / LINEAR FOon BLOCK (GALLONS / LINEAR Foon (ASSUMING 40% POROSITY) ei" · 0.16) ~== =~:" HOLE: 0.52AIRLIFT --4" • 0.65 G-::-.. 1101.E -ii:ii> 6" • 1.47 4" CASING AND 10" HOLE" 1.37 OTHER ...,,..., 4" CASING AND 12" HOLE = 2.09 HOLEDIAMffiR dh =~ --I d W14-;0UNI WELL VOLUME CALCUUTION: ~ -~_f of-.scY-een WELL CASING _...,. SURFACE INSIDE DIAMffiR dwlD: __ ! l CASING VOLUME =Vc=ir(dwJ 0 J2 (To-H)=3.14(-2-) 2 OUTSIDE DIAMETER dw OD = L FILTER PACK [(~ 2 (dw00t]( *)( ) DEPTH TO: H = o/h.&, 1 1-> js PORE VOLUME = Vt = ir 2 ) ---r TD-(Sor H) P = 1WATERLEVEL if S>H use S, if S<H use H.) TD BASE OF SEAL : ·: ? t:.;il}--3.14[(-2-l2-(-2-l2] ( )( )= - BASE OF WELL INTERVAi. TOTAL WELL VOLUME =VT= Vt +Ve= + : --ft.3 X 7.48 : __ gal. EST. FILTER PACK ---1 dh I-POROSITY p = DEVELOPMENT LOG: iNf,.,.,AL<-. CUMULATIVE WATER QUALITY COMMENTS: - FLOW WATER TIME ELAPSED REMOVEDDATEMETHODRATEBEGJNiENDTIME (gpm) GALLONS pt CONDUCTIVITY TURBIDITY TEMP. l7-f1,1& i3 3.ip ~;I a k'-5Jl, ~~ ~.7.3 /3.D very .cl. 1¢. 'I (BEGIN) t .. "1111 1.35'2 .. 12 1. zz. S-.1,"1 /~ . .3"f ' I 15.2 I 'Ir/¢' 30 zg s.~, 13. '1-3 II 1/R. 't I J'I .3 I I /,,:, l 32. 5.t,£1 13. 21 ,iqcd' 14, / 1~31 (p 7-51~ IS.:5"\ ,s .. :s-; ,, t7()-t> Al~ rg~i~t<.> 1'-153 S3 35" ~. {'2. 12-78 ti 1/. 4> lf 5c, Be., 35S s.~3 (l-~;> ,, IP1-1 Jl/51 g1 31 ~.s, is. iPB 'I ~1.1> 15¢2 q:i 3g' r;. </I, ,~, 2.'f \! t,'/. '1 15¢# qi.j Lf 2-s.4./'f ? &4I -. II ~'/.1 J5ri>t '11 21 tf {,.1/S' 12-~1 I• ,1. g V ,sen ,v 11 "v 'f(p ~-'1/p ,3. t:}2-!I 1£7, I I I I I I I I I I I. I I I I I I I I I OGDEN ••••• WELL DEVELOPMENT JOBNCI. rlTE WELLNO. • J M1.A) -Jbq-- PREPARED BY ~ ' v~ r:, METHOD: OVERPUMPAGE-----, s. 4 IS 9 . REMARKS: .INmAL WATER LEVEL I BAILER SURGE BLOCK v FINAL WATER LEVEL ----- CAPACITY OF CASING VOLUME BETWEEN CASING AND HOLE (GALLONS/ UNEAR FOon ASSUMING 4ft. POROSITY) (GALLONS / LINEAR FOOT) 2· • 0.16 2" CASING AND 6" HOLE • D.52 AIR LIFT OTHER HOLEDIAMmR llURFACIWELLCASING ~ ...,. INSIDE DIAMmR dw ID= __ f l OUTSIDE DIAMETER dw OD ,. ~ JH DEPTHTO: H .. 1ctT' _ ~sWATERLEVEL .J TD s_·?,' /1 BASEOFWELL TD • ~e:;;,•5° • }=-:: EST. FILTER PACK __J I-- POROSITY P ,. __ --1 d h BASE OF SEAL DEVELOPMENT LOG: DATE TIME METHODBEGl~END aAPSED ROW RATETIMEPl A 12-91,o J4oo lk.-J 0 BEGIN) 1Mc Ao A4-~ 4< A~v ~o A~5" ,;~ A-5'lf 5't:t l f;° ID 7C' 2v io t51.~ Ss" f5'6D ~D 5;; '7 3 Je,g 1~5"1 ) \ l v ltooo ,1 ) -irJ, 4• • 0.65 2" CASING AND 8" HOLE• 0.98 6" • 1.47 4" CASING AND 10" HOLE• 1.37 If' CASING AND 12" HOLE :s 2.09 WELL VOLUME CALCULATION: cAs1NGvoLuME =Vc=ir(¥.)2 (ro-H) .. 3.14(-2-)2( - ) • --- Fl~l,\~~icL~ME =Vt =ir[(2f)2-(~)2}ro-(sorH)*)(P)= if S>H uses, ifS<H useH.) 3.14[(-2-)2 -(-2-t] ( -) ( ) = -- TOTAL WELL VOLUME ,. Vy= Vt +Ve= + s __ ft.3xl48 = __ gal. CUMULATIVE WATER WATER QUALITY COMMENTS: REMOVED GALLONS If! CONDUCTIVITY TURBIDITY TEMP. Io rr.r7 ,.10 ZC> o.c:r-, 7,~ l41 j,=f ?CJ M ,',,J 5. zr Jo 1~ s- 37 74·7 b,£>5 v. Cf(-,, 15'·) r1 t.~o t:). cc b 4c-!,'17 p.qs- ti 5'.'lte, 0-75' 12-G.'f5 0-'!S- I OGDEN .II WELL PROJECT ff /1,o() I/ .-V, ./.J tf£: WEl.LNO. IM lA.)-d>S- I I I I I I I I I I I I I I I I _,_ I DEVELOPMENT JOBNO. ,, rlTE PREPARED BY.~ ~ ... ; METHOD: OVERPUMPAGE · INmAL WATER LEVEL · 1 ~ . ' /5/;,.t:; REMARKS: BAILER v-RNAL WATER LEVEL SURGE v CAPACITY OF CASING VOLUME BETWEEN CASING AND HOLE (GALLONS/ LINEAR FOon BLOCK (GALLONS / LINEAR Foon (ASSUMING 40% POROSITY) t(? ,(/I•~-~ 2" • 0.16 2• CASING AND s• HOLE : D.52 AIR LIFT 4" • 0.65 2" CASING AND 8" HOLE : 0.98 6" • 1.47 4• CASING AND 10" HOLE • 1.37 OTHER 4• CASING AND 12" HOLE• 2.09 HOLE DIAMETER dh ~ --i .d w~ OIIOUND WELL VOLUME CALCULATION: WELL CASING ~ ...,-SUR1ACI CASING VOLUME =Vc=r(dwJD)2 (TD-H)=3.14(-2-}2( ) . INSIDE DIAMETER dw -~ t l - II H OUTSIDE DIAMETER dw OD =L J s FILTER PACK [(~b-)2 (dw00t]( *)( ) DEPTHTO: 74 ) ~ PORE VOLUME = Vt = r 2 ---r-TD-(Sor H) . P = WATER LEVEL H : tti ,- if S>H use S, if S<H use H.) TD BASE OF SEAL s. -1 : 3.14[(-2-}2-(-2-t] ( ) ( )= ) . - BASEOFWELL TD 0 ti I}----: ' INTlRYAL ft.3x7.48 • __ gal. TOTAL WELL VOLUME =Vy= Vt+ Ve= + EST. FILTER PACK p = ----l dh ~ POROSITY DEVELOPMENT LOG: CUMULATIVE WATER QUALITY COMMENTS: FLOW WATER DATE TIME METHOD ELAPSED RATE REMOVED •. BEGINiEND TIME (gpmf GALLONS pl CONDUCTIVITY TURBIDITY TEMP. - l-12,.n: jfp',.~ .. b~;) 0 I).~ f.lJz ~-'3c..--y. /; '10 .. ~ v. v~t-;') (BEGIN) ~J~ ., 1b<~1 3 \~ r-SJ \A .4.z.. ·McO. ,p,.fj t;> -lJ /;a) 5-. Jt;,k"' 5 ;;., 5".~ j 14 -7~ h}.o Jb',~ b ,4-r-;i! )~·00 I:;,)' b, 4·5"" ;.,~ )§.'J.5' '12. .,:;; fk,:·~ ID IS S-'f/1 \ S", ~) ~-4- 1b;4-r I 5'° I lo f,S'i, 1r.q¢ ti,2. (p i1::·,,v -~o t+ ;.'DS Jb· ~ J bZ-1/ Jb'-.,5 ,1 ~~ t 'iS 5'.;.z ) b,. 6""5" ,v ~2., I I I I I I I I OGDEN DATE/TIME O~n 03Y 050 IO '5'""'> llOO l 03 l l 0 I l 5 11 ?_0 GROUND-WATER SAMPLING LOG San Diego County (SA/M Guidelines) GALLONS REMOVED i 0 l :5 TEMP(°C) O.+ 2 n. "2- 2. l. 3 2 I A 23.o pH to.~ 5 o .O\(p q 4 i°i SP.COND. iSoo TURBIDITY V ..., I I I d-ra....;c\_owf' C\ ('Cl.\{ C. W V... e_ "1 CU--V / 0 d I O.(O..'f C.\Ou~11 r-l~"-r I'\~ I\~ Ol;..0..../ LJ l"\rQLA)~l.._',f") Q.: t- f\,J a ~ ol,-a_ o _ . TURBIDITY ""'-0 9: · pH ---7::~-....::;'2....;;::...i..1 ---------- SEDIMENT vY'\C c.\. · SP.COND. ----~~O;;..;;D=...O..._ _______ _ OTHER:. Sa\ u.rn l 1 ,-. e r TRANSPORTER: --------- TIME:-------- I CAPACITY OF CASING (GALLONS/LINEAR FOOT) 2"-0.16 • 4"-0.65 • 6"~1.47 • 8"-2.6~ • 10"-4.08 • 12"-5.87 VOLUME BETWEEN CASING AND HOLE (GALLONS/LINEAR FOOT) (ASSUMING_40%_eoaosn:¥)--------- 2"-CASlNG-AN[)-6"-H0L:E-=0:52----4n-cASING-AND10"HOLE = 1.37 I 2"' CASING 8" HOLE -0.98 4" CASING AND 12" HOLE= 2.09 I I I I I I I I I I I I I I I I I OGDEN ••••• GROUND-WATER SAMPLING LOG San Diego County (SA/M Guidelines) WELL No. fY) w , o z LOCATION: 6 r °' (\ c ~ '::\J \ t'f. PROJECT NO. DATE: fl • Jal: • °I (f TIME: l I Y S CLIMAtlC CONDITIONS: ------- TOTAL DEPTH: QO.OSsTATIC WATER LEVEL: L\0-'6(o LENGTH OF SATURATED ZONE: 9 ,1 '\ SAMPLE WITHDRAWAL METHOD: '''"'0i~5f!!~~-O COLOR \o ,("i:) u.).('"\ TEMP. ----~--9, ......... _:): _________ _ TURBIDITY fV\.03:: pH __ __,3:,..._.;...• "3...._]:.___ ________ _ SEDIMENT \'Y\O~ SP.COND. __ __...3...._..Q"'"'O~O----------- OTHER: LABORATORY ANALYSIS PARAMETERS AND PRESERVATIVES: ------------,---- 0\Jw-\ NUMBER AND TYPES OF SAMPLE CONTAINERS USED: ----------------- SAMPLE IDENTIFICATION NUMBER($) AND TIME: ----'-C0........_,...,.4.._)~0~"2..=--------S==..,.;;;O~\---"'M-...:..---"-1 """\.D'""'I .... S...._ __ DECONTAMINATION PROCEDURES: ----------------------- NOTES=-------------------------------- SAMPLED BY:. _ _.___,_.,--+-=--=----------...--------------- SAMPLES DELIVERED TO: ------------,RANSPORTER: --------- DATE: ---------TIME: -------- 15 I CAPACITY OF CASING (GALLONS/LINEAR Foon 2i'-0.16 • 4"-0.65 • 611:.1.47 • 8"-2.61 • 10"-4.08 • 12"-5.87 VOLUME BETWEEN CASING AND HOLE (GALLONS/LINEAR FQ__O_T)_(ASSUMING_40%-EOROSIT¥)-----,------------ 2°-cASli'·JG-AND-611 RO(E-;-0.52 4" CASING AND 10" HOLE= 1.37I2"' CASING 8" HOLE -0.98 4" CASING AND 12" HOLE = 2.09 I I I I I I I I I I I I I I I I I I I OGDEN ••••• GROUND-WATER SAMPLING LOG San Diego County (SA/M Guidelines) BOREHOLE VOLUME: CAPAC1TY OF;;Sl~fi~~~~~I~i;i''ij (GalsJLinear Fl)+VOLUME BETWEEN CASING AND HOLE O ·! ~ (Gals./Unear Ft.)= /. / q GALS/LINEAR FT. VOLUME OF WATER · VACUATED: ~ f!t_ GALS/LINEAR FT. X LENGTH OF SATURATED ZONE /21_"1:_ LINEAR FT. well) OR 1.5 (Fast ?ell, stablep¥i3meters) OR 3 (Fast well, unstable· parameters) = 3i$]4 .JGALS. D OF REMOVAL; (..2 YJ4 v1 d_.f:!Q. 5 PUMPING RATE:------- NUMBER AND TYPES OF SAMPLE CONTAINERS USED: ----------------- SAMPLE IDENTIFICATION NUMBER(;) AND TIME: __.M-'--""W:...:..:O:;...!> ... ·"'---...;;;:~--..-.-+\--'oJ.-.._.,._._( jf.....__~~ .... ,-_.-___ _ DECONTAMINATION PROCEDURES: ----------------------- NOTES=------------------------------------ SAMPLED BY: iY\£ l S C • SAMPLES DELIVERED TO: ______ r __ L_I ____ TRAN.SPORTER: --------- DATE: ---------TIME: -------- CAPACITY OF CASING (GALLONS/LINEAR Foon 2"-0.16 • 4"~0.65 • 6"-1.47 • .. 8"-61 • 10"-4.08 -• 12"-5.87 VOLUME BETWEEN CASING AND HOLE (GALLONS/LINEAR FOOT)_(AS.S_UMING..40% __ 2" eASING-AND-611 -HOtE---;;0~52~---4,;-CASING AND 10" HOLE = 1.37 2"' CASING 8" HOLE -0.98 4" CASING AND 12" HOLE =: 2.09 I I I I I I I I I I I I I I I I I OGDEN ••••• GROUND-WATER SAMPLING LOG San Diego County (SA/M Guidelines) BOREHOLE VOLUME: CAPACITY OF (GalsJLinear Ft.)+VOLUME BETWEEN CASING AND HOLE D .-q ~ (GalsJLinear Ft.)= FT. VOLUME OF WATER G EVACUATED: \ ,N GALS/LINEAR FT. X LENGTH OF SATURATED ZONE\0 ,0(.p LINEAR FT. low well) OR 1.5 (Fast well, stable pjlfameters) OR 3 (Fast well, unstable parameters) = \ \ , Y lti GALS. HOD OF REMOVAL:k) C \ U)s.\k'()S. PUMPING RATE:------ ii14iR~§i3e6XfAf DATE/TIME GALLONS TEMP(°C) pH SP.COND. TURBIDITY REMOVED --~ ......... l+l"° ':.:) "2..1 1-u,, -~'r C,Z:.ObO 'l'\Oo -h,' .\ ~,:~., I+-\~ lf -Z I.\ "1.dert -:f"-)oo m.r-A -V\. ~ "'-~" .- l r-2 \ fn °':).( ~ <:j< t"'JC;O C"' ,I,, ant\. 0\ 'rl\-l'Ot I.) 22.-Z... It~ q ; "2 '2.. 0 +.o°\ 'b 300 ~u I~ 2v, l? ¥·7 -:+ .a":+-iooo Lev.., -<U...o 41....__/ l-Zt\ 14 3.oo 1-.0lo °IOOo lov..J -~ c\;r ~oo~-a..,\-1'4 siNii?.teoiii >ii_---- SAMPLE WITHDRAWAL METHOD: ---~-A-~-.... -_S ____ ~ ...... -·--=----~ ........... ---------------- COLOR · X)fvw\'\ TEMP. "20, I TURBIDITY \.SJ ~ pH :;b,\ re> SEDIMENT V\.; 1::V\ SP.COND. - OTHER: LAB~AT~SARAMETER~ A~D PRESERVATIVES: ~:...1..::....-+....i.»o'-=~-+--~""'-'-........ -:...;;a.,,:.J.-. SAMPLE IDENTIFICATION NUMBER(S) AND TIME: _r_Y\....a.WOO_.;;;._a...-__..;;S~:o---4le-----(...::~-------l4......,.3......_0 ______ _ DECONTAMINATION PROCEDURES: ---------------------- NOTES=------------------------------- SAMPLED BY:_M___,'""---t-a....-..._.,...:..:,._ ... " -------------....--------- SAMPLES DELIVERED T --,.,,!!,' .....,.f'._:-{_-________ TRANSPPR1ER: · --------- DATE:--------- I CAPACITY OF CASIN -bNS/LINEAR Foon 2'i-0.16 • 4"-0.65 • 6"-1.47 • 8"-2.61 • 10"-4.08 • 12"-5.87 VOLUME BETWEE _ __§~G AND HOLE_(GALLOl"l!S/LINEARF:OOT)-(ASSIJMING-40%-P0R0SITY)-~ ~---- 211 -CAS1NG7, -. 6" i40LE =0.52 4" CASING AND 10" HOLE = 1.37 2"' CASING ~ HOLE -0.98 4" CASJNG AND 12" HOLE = 2.09 . . I• :• • ~ ~· •' I .' I ,' I • I I I I I I I Ie I Ii c..J 0 ls ,~ Ii I I I OGDEN ••••• GROUND-WATER SAMPLING LOG San Diego County (SA/M Guidelines) WELL NO. nt""'?f' LOCATilff/ti /3.-,anJv u./ YJ4!. PROJECT NO.--·------ DATE: i<Z-1-~ ~ . TIME: / ~/ s-cifMATIC CONDITIONS: (!,0011 t::./t:J-<..J Y TOTAL DEPTH: 1$s"" STATIC WATER LEVEL: 7S, 't? LENGTH OF SATURATED ZON{ 1 /-Zf LINEAR FT. wEtcieueoatJe r BOREHOLE VOLUME: CAPACITY OF CASING ~: fk y (GalsJLinear Ft.)+VOLUME BETWEEN CASING AND HOLE ~ · ·nB' (GalsJLinear Ft.)= t. / 'f GALS/LINEAR FT. ~O~ OF WATER TO-BE EVACUATED: ~, t"'!f. GALS/LINEAR FT. X LENGTH OF SATURATED ZONE £... LINEAR FT. slow well) OR 1.5 (Fast well, stable parameters) OR 3 (Fast well, unstable parameters)= 12. "7 GALS. ifETHOD OF REMOVAL: t::.c,~ PUMPING RATE:------- DATE/TIME 2. SAMPLE WITHDRAWAL M~:::~e~:fi'~~~~~0 242522222 COLOR 0~ TEMP. __ "'"13:-:~~'-\...._\ _________ _ TURBIDITY m~~ pH \,a,9,4 SEDIMENT ~~-SP.COND. ----"---------------- OTHER: ' LABORATORY ANALYSIS PARAMETERS AND PRESERVATIVES: ------------------ SQQ_ ffi\)() \ NUMBER AND TYPES OF SAMPLE CONTAINERS USED: ----------------- SAMPLE IDENTIFICATION NUMBER($) AND TIME: __ t'<)'---'...,.,,Q-.,-O-=-ct~---~---:C)=-\---"AA-=--___ \_O. .... CQ ___ _ DECONTAMINATION PROCEDURES: ------------------------- NOTES=-------------------------------- SAMPLED BY: ffi \) 1 ~~ SAMPLES DELIVERED TO: ____________ TRANSPORTER: --------- DATE:---------TIME: --------· 1 CAPACITY OF CASING (GALLONS/LINEAR Foon 2"-0.16 • 4"-0.65 • 6"-1.47 • 8"-2.61 • 10"-4.08 • 12"-5.87 VOLUME BETWEEN CASING AND HOLE (GALLONS/LINEAR FOOT) (ASSUMING 40% POROSITYL~ ·------·. 2.!!...CASING-AND6"-H0l£-=0:52---4" CASING-AND-ro"-RO[E = 1.37 I 2"' CASING 8" HOLE -0.98 4" CASING AND 12" HOLE = 2.09 I I I I I I I I I I I I I I I I I I I APPENDIX B ANALYTICAL LABORATORY REPORTS I I I I I I I I I I I I I I I I I Date: 02-26-1996 CKY Batch No.: 96B085 Attn: Don Barrie Ogden Environmental 5510 Morehouse Drive San Diego, CA 92121 Subject: Lab9ratory Report. ProJect: Brandywine CK Y incorporated Analytical Laboratories Enclosed is the Laboratory report for samples received on 02/19/96. The samples were received in coolers with ice and intact; the chain-of-custody forms were properly filled out. The data reported include : Sample ID Control No. -------------------- BWBSOlSOlDlO.O B085-01 BWBS01S02D71 B085-02 BWBS02S01Dll.O B085-03 BWBS02S02D56.0 B085-04 BWBS03S01D10.5 B085-05 BWBS03S02D66.5 B085-06 BWBS03S03D75.5 B085-07 Matrix Soil Soil Soil Soil Soil Soil Soil Analysis EPA EPA TOC EPA EPA TOC EPA EPA TOC EPA EPA TOC EPA EPA TOC EPA EPA TOC EPA EPA TOC 8010 8020 8010 8020 8010 8020 8010 8020 8010 8020 8010 8020 8010 8020 The results are summarized on the following pages. Please feel free to call if you have any questions concerning these results. Sincerely yours, c_ __ (( ___ i!~-- Kam Y. Pang, Ph.b. Laboratory Director P.S. -All analyses requested for the above referenced project have been completed. Therefore, unless instructed, the remaining Qortions of the samples will be disposed after fifteen (15) days rrom the date of this report. I ~-----------------~----~---- I 630 Maple Ave., Torrance, Calif. 90503 • Telephone 310-618-8889 • Fax: 310-618-0818 I I I I I I I I I I I I I I I I I I EPA METHOD 8010 HALOGENATED VOLATILE ORGANICS CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO. : MOISTURE: Ogden Environmental Brandywine 96B085 BWBSOlSOlDlO.O B085-0l 8.7 DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: 02/17/96 02/19/96 NA 02/21/96 SOIL 1 RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Dichlorodifluoromethane ND 27.4 Chloromethane ND 27.4 Vinyl Chloride ND 27.4 Bromomethane ND 27.4 Chloroethane ND 27.4 Trichlorofluoromethane ND 5.48 1,1-Dichloroethene ND 5.48 Meth1lene Chloride ND 27.4 cis~ ,2-Dichloroethene ND 5.48 trans-lh2-Dichloroethene ND 5.48 lhl-Dic loroethane ND 5.48 C loroform ND 5.48 1,161-Trichloroethane ND 5.48 Car on Tetrachloride ND 5.48 1,2-Dichloroethane ND 5.48 Trichloroethene ND 5.48 1 1 2-Dichloropropane ND 5.48 D1bromomethane ND 5.48 Bromodichloromethane ND 5.48 2-Chloroethyl vinylether ND 5.48 trans-1,3-Dichloropropene ND 5.48 cis-1,3-Dichloro~ropene ND 5.48 1,1,2-Trichloroe hane ND 5.48 Tetrachloroethene ND 5.48 1,3-Dichloropro~ane ND 5.48 1 1 1,1,2-Tetrach oroethane ND 5.48 D1bromochloromethane ND 5.48 Ethylene Dibromide ND 5.48 Chlorobenzene ND 5.48 Bromoform ND 5.48 lhl,2,2-Tetrachloroethane ND 5.48 C lorotoluene ND 5.48 1,3-Dichlorobenzene ND 5.48 1,4-Dichlorobenzene ND 5.48 1,2-Dichlorobenzene ND 5.48 Benzylchloride ND 5.48 SURROGATE PARAMETER 9- 0 RECOVERY QC LIMIT -------------------------------- Bromofluorobenzene 84 60-140 MDL: Method Detection Limit I ~ · CKY INC., ANALYTICAL 1.ABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618.·8889 Fax: (310) 618-0818 I I I I I I I I I 1. I I I I I I I I EPA METHOD 8010 HALOGENATED VOLATILE ORGANICS CLIENT: Ogden Environmental DATE COLLECTED: 02/17/96 PROJECT.: Brandywine DATE RECEIVED: 02/19/96 BATCH NO.: 96B085 DATE EXTRACTED: NA SAMPLE ID: BWBS01S02D71 DATE ANALYZED: 02/20/96 CONTROL NO.: B085-02 MATRIX: SOIL MOISTURE: 24.3 DILUTION FACTOR: 1 RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Dichlorodifluoromethane ND 33 Chloromethane ND 33 Vinyl Chloride ND 33 Bromomethane ND 33 Chloroethane ND 33 Trichlorofluoromethane ND 6.61 1,1-Dichloroethene ND 6.61 Meth1lene Chloride ND 33 cis-,2-Dichloroethene ND 6.61 trans-lh2-Dichloroethene ND 6.61 lhl-Dic loroethane ND 6.61 C loroform ND 6.61 1,1,1-Trichloroethane ND 6.61 Carbon Tetrachloride ND 6.61 1,2-Dichloroethane ND 6.61 Trichloroethene ND 6.61 1 1 2-Dichloropropane ND 6.61 D1bromomethane ND 6.61 Bromodichloromethane ND 6.61 2-Chloroethyl vinylether ND 6.61 trans-1,3-Dichloropropene ND 6.61 cis-1,3-Dichlorofropene ND 6.61 1,1,2-Trichloroe hane ND 6.61 Tetrachloroethene ND 6.61 1,3-Dichloropro~ane ND 6.61 1 1 1,1,2-Tetrach oroethane ND 6.61 D1bromochloromethane ND 6.61 Ethylene Dibromide ND 6.61 Chlorobenzene ND 6.61 Bromoform ND 6.61 lhl,2,2-Tetrachloroethane ND 6.61 C lorotoluene ND 6.61 1,3-Dichloroben~ene ND 6.61 1,4-Dichlorobenzene ND 6.61 1,2-Dichlorobenzene ND 6.61 Benzylchloride ND 6.61 SURROGATE PARAMETER % RECOVERY QC LIMIT ----------------------------- - - - Bromofluorobenzene 68 60-140 MDL: Method Detection Limit I~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave., Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I I I EPA METHOD 8010 HALOGENATED VOLATILE ORGANICS CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL. NO . : MOISTURE: Ogden Environmental Brandywine 96B085 BWBS02S01Dll.O B085-03 14.0 DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: 02/17/96 02/19/96 NA 02/20/96 SOIL 1 RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Dichlorodifluoromethane ND 29.1 Chloromethane ND 29.1 Vinyl Chloride ND 29.1 Bromomethane ND 29.1 Chloroethane ND 29.1 Trichlorofluoromethane ND 5.81 1,1-Dichloroethene ND 5.81 Methilene Chloride ND 29.1 cis-,2-Dichloroethene ND 5.81 trans-lh2-Dichloroethene ND 5.81 lhl-Dic loroethane ND 5.81 C loroform ND 5.81 1,1,1-Trichloroethane ND 5.81 Carbon Tetrachloride ND 5.81 1,2-Dichloroethane ND 5.81 Trichloroethene ND 5.81 1<2-Dichloropropane ND 5.81 D1bromomethane ND 5.81 Bromodichloromethane ND 5.81 2-Chloroethyl vinylether ND 5.81 trans-1,3-Dichloropropene ND 5.81 cis-1,3-Dichlororropene ND 5.81 1,1,2-Tric-hloroe hane ND 5.81 Tetrachloroethene ND 5.81 1,3-Dichloropro~ane ND 5.81 1<1,1,2-Tetrach oroethane ND 5.81 D1bromochloromethane ND 5.81 Ethylene Dibromide ND 5.81 Chlorobenzene ND 5.81 Bromoform ND 5.81 lhl,2,2-Tetrachloroethane ND 5.81 C lorotoluene ND 5.81 1,3-Dichlorobenzene ND 5.81 1,4-Dichlorobenzene ND 5.81 1,2-Dichlorobenzene ND 5.81 Benzylchloride ND 5.81 SURROGATE PARAMETER % RECOVERY QC LIMIT ---------------------------- - - - - Bromofluorobenzene 82 60-140 MDL: Method Detection Limit I G\, CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave., Torrance. Calif. 90503 TeL (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I I I EPA METHOD 8010 HALOGENATED VOLATILE ORGANICS CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO . : MOISTURE: Ogden Environmental Brandywine 96B085 BWBS02S02D56.0 B085-04 24.1 DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: 02/17/96 02/19/96 NA 02/20/96 SOIL 1 RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Dichlorodifluoromethane ND 32.9 Chloromethane ND 32.9 Vinyl Chloride ND 32.9 Bromomethane ND 32.9 Chloroethane ND 32.9 Trichlorofluoromethane ND 6.59 1,1-Dichloroethene ND 6.59 Meth1lene Chloride ND 32.9 cis-,2-Dichloroethene ND 6.59 trans-lh2~Dichloroethene ND 6.59 lhl-Dic loroethane ND 6.59 C loroform ND 6.59 1,1,1-Trichloroethane ND 6.59 Carbon Tetrachloride ND 6.59 1,2-Dichloroethane ND 6.59 Trichloroethene ND 6.59 1 1 2-Dichloropropane ND 6.59 Dibromomethane ND 6.59 Bromodichloromethane ND 6.59 2-Chloroethyl vinylether ND 6.59 trans-1,3-Dichloropropene ND 6.59 cis-1,3-Dichlorofropene ND 6.59 1,1,2-Trichloroe hane ND 6.59 Tetrachloroethene ND 6.59 1,3-Dichloropro~ane ND 6.59 1 1 1,1,2-Tetrach oroethane ND 6.59 Dibromochloromethane ND 6.59 Ethylene Dibromide ND 6.59 Chlorobenzene ND 6.59 Bromoform ND 6.59 lhl,2,2-Tetrachloroethane ND 6.59 C lorotoluene ND 6.59 1,3-Dichlorobenzene ND 6.59 1,4-Dichlorobenzene ND 6.59 1,2-Dichlorobenzene ND 6.59 Benzylchloride ND 6.59 SURROGATE PARAMETER % RECOVERY QC LIMIT --------- --------- Bromofluorobenzene 86 60-140 MDL: Method Detection Limit CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618·8889 Fax: (310l 618-0818 I 1· I I I I I I I I I I I I I I I I EPA METHOD 8010 HALOGENATED VOLATILE ORGANICS CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO . : MOISTURE: Ogden Environmental Brandywine 96B085 BWBS03S01D10.5 B085-05 11. 9 DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: 02/18/96 02/19/96 NA 02/20/96 SOIL 1 ==================================================================== RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Dichlorodifluoromethane ND 28.4 Chloromethane ND 28.4 Vinyl Chloride ND 28.4 Bromomethane ND 28.4 Chloroethane ND 28.4 Trichlorofluoromethane ND 5.68 1,1-Dichloroethene ND 5.68 Meth1lene Chloride ND 28.4 cis-,2-Dichloroethene ND 5.68 trans-lh2-Dichloroethene ND 5.68 lhl-Dic loroethane ND 5.68 C loroform ND 5.68 1,1,1-Trichloroethane ND 5.68 Carbon Tetrachloride ND 5.68 1,2-Dichloroethane ND 5.68 Trichloroethene ND 5.68 1,2-Dichloropropane ND 5.68 Dibromomethane ND 5.68 Bromodichloromethane ND 5.68 2-Chloroethyl vinylether ND 5.68 trans-1,3-Dichloropropene ND 5.68 cis-1,3-DichloroEropene ND 5.68 1,1,2-Trichloroe hane ND 5.68 Tetrachloroethene · ND 5.68 1,3-Dichloropro~ane ND 5.68 1,1,1;2-T~trach oroethane ND 5.68 Dibromochloromethane ND 5.68 Ethylene Dibromide ND 5.68 Chlorobenzene ND 5.68 Bromoform ND 5.68 lhl,2,2-Tetrachloroethane ND 5.68 C lorotoluene ND 5.68 1,3-Dichlorobenzene ND 5.68 1,4-Dichlorobenzene ND 5.68 1,2-Dichlorobenzene ND 5.68 Benzylchloride ND 5.68 SURROGATE PARAMETER % RECOVERY QC LIMIT ------------------------------- - Bromofluorobenzene 85 60-140 MDL: Method Detection Limit CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I I I EPA METHOD 8010 HALOGENATED VOLATILE ORGANICS CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO . : MOISTURE: Ogden Environmental Brandywine 96B085 BWBS03S02D66.5 B085-06 22.7 DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: 02/18/96 02/19/96 NA 02/20/96 SOIL 1 RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Dichlorodifluoromethane ND 32.3 Chloromethane ND 32.3 Vinyl Chloride ND 32.3 Bromomethane ND 32.3 Chloroethane ND 32.3 Trichlorofluoromethane ND 6.47 1,1-Dichloroethene ND 6.47 Meth1lene Chloride ND 32.3 cis-,2-Dichloroethene ND 6.47 trans-lh2-Dichloroethene ND 6.47 lhl-Dic loroethane ND 6.47 C loroform ND 6.47 1,1,1-Trichloroethane ND 6.47 Carbon Tetrachloride ND 6.47 1,2-Dichloroethane ND 6.47 Trichloroethene 77 6.47 1<2-Dichloropropane ND 6.47 Dibromomethane ND 6.47 Bromodichloromethane ND 6.47 2-Chloroethyl vinylether ND 6.47 trans-1,3-Dichloropropene ND 6.47 cis-1,3-Dichloro~ropene ND 6.47 1,1,2-Trichloroe hane 12 6.47 Tetrachloroethene ND 6.47 1,3-Dichloropro~ane ND 6.47 1<1,1,2-Tetrach oroethane ND 6.47 Dibromochloromethane ND 6.47 Ethylene Dibromide ND 6.47 Chlorobenzene ND 6.47 Bromoform ND 6.47 lhl,2,2-Tetrachloroethane ND 6.47 C lorotoluene ND 6.47 1,3-Dichlorobenzene ND 6.47 1,4~Dichlorobenzene ND 6.47 1,2-Dichlorobenzene ND 6.47 Benzylchloride ND 6.47 SURROGATE PARAMETER % RECOVERY QC LIMIT -------------------------------- Bromofluorobenzene 84 60-140 MDL: Method Detection Limit I ~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave., Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 6 l8-il818 I I I I I I I I I I I I I I EPA METHOD 8010 HALOGENATED VOLATILE ORGANICS CLIENT: Ogden Environmental DATE COLLECTED: 02/18/96 PROJECT: Brandywine DATE RECEIVED: 02/19/96 BATCH NO. : 96B085 DATE EXTRACTED: NA SAMPLE ID: BWBS03S03D75.5 DATE ANALYZED: 02/20/96 CONTROL NO.: B085-07 MATRIX: SOIL MOISTURE: 19.7 DILUTION FACTOR: 1 RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Dichlorodifluoromethane ND 31.1 Chloromethane ND 31.1 Vinyl Chloride ND 31.1 Bromomethane ND 31.1 Chloroethane ND 31.1 Trichlorofluoromethane ND 6.23 1,1-Dichloroethene ND 6.23 Meth1lene Chloride ND 31.1 cis-,2-Dichloroethene ND 6.23 trans-lh2-Dichloroethene ND 6.23 lhl-Dic loroethane ND 6.23 C loroform ND 6.23 1,1,1-Trichloroethane ND 6.23 Carbon Tetrachloride ND 6.23 1,2-Dichloroethane ND 6.23 Trichloroethene 6.3 6.23 lc2-Dichloropropane ND 6.23 D1bromomethane ND 6.23 Bromodichloromethane ND 6.23 2-Chloroethyl vinylether ND 6.23 trans-1,3-Dichloropropene ND 6.23 cis-1,3-Dichloro~ropene ND 6.23 1,1,2-Trichloroe hane ND 6.23 Tetrachloroethene . ND 6 .23 1,3-Dichloropro~ane ND 6.23 lcl,1,2-Tetrach oroethane ND 6.23 D1bromochloromethane ND 6.23 Ethylene Dibromide ND 6.23 Chlorobenzene ND 6.23 Bromoform ND 6.23 lhl,2,2-Tetrachloroethane ND 6.23 C lorotoluene ND 6.23 1,3-Dichlorobenzene ND 6.23 1,4-Dichlorobenzene ND 6.23 1,2-Dichlorobenzene ND 6.23 Benzylchloride ND 6.23 SURROGATE PARAMETER % RECOVERY QC LIMIT ----------------------------- - - - Bromofluorobenzene 88 60-140 MDL: Method Detection Limit 1 G\, CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310l 618-0818 I I I I I I I I I I I I I I I I I I I EPA METHOD 8010 HALOGENATED VOLATILE ORGANICS CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO . : MOISTURE: Ogden Environmental Brandywine 96B085 MBLKlS VAL617B NA DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: NA NA NA 02/19/96 SOIL 1 RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Dichlorodifluoromethane ND 25 Chloromethane ND 25 Vinyl Chloride ND 25 Bromomethane ND 25 Chloroethane ND 25 Trichlorofluoromethane ND 5 1,1-Dichloroethene ND 5 Meth1lene Chloride ND 25 cis-,2-Dichloroethene ND 5 trans-lh2-Dichloroethene ND 5 lhl-Dic loroethane ND 5 C loroform ND 5 1,1,1-Trichloroethane ND 5 Carbon Tetrachloride ND 5 1,2-Dichloroethane ND 5 Trichloroethene ND 5 1,2-Dichloropropane ND 5 Dibromomethane ND 5 Bromodichloromethane ND 5 2-Chloroethyl vinylether ND 5 trans-1,3-Dichloropropene ND 5 cis-1,3-Dichlororropene ND 5 1,1,2-Triohloroe hane ND 5 Tetrachloroethene ND 5 1,3-Dichloropro~ane ND 5 1 1 1,1,2-Tetrach oroethane ND 5 Dibromochloromethane ND 5 Ethylene Dibromide ND 5 Chlorobenzene ND 5 Bromoform ND 5 lhl,2,2-Tetrachloroethane ND 5 C lorotoluene · ND 5 1,3-Dichlorobenzene ND 5 1,4-Dichlorobenzene ND 5 1,2-Dichlorobenzene ND 5 Benzylchloride ND 5 SURROGATE PARAMETER % RECOVERY QC LIMIT ------------------------------- - Bromofluorobenzene 119 60-140 MDL: Method Detection Limit CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .• Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I I I EPA METHOD 8010 HALOGENATED VOLATILE ORGANICS CLIENT: Ogden Environmental DATE COLLECTED: NA PROJECT: Brandywine DATE RECEIVED: NA BATCH NO.: 96B085 DATE EXTRACTED: NA SAMPLE ID: MBLK2S DATE ANALYZED: 02/21/96 CONTROL NO.: VAL617B3 MATRIX: SOIL MOISTURE: NA DILUTION FACTOR: 1 RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Dichlorodifluoromethane ND 25 Chloromethane ND 25 Vinyl Chloride ND 25 Bromomethane ND 25 Chloroe thane ND 25 Trichlorofluoromethane ND 5 1,1-Dichloroethene ND 5 Meth1lene Chloride ND 25 cis-,2-Dichloroethene ND 5 trans-lh2-Dichloroethene ND 5 lhl-Dic loroethane ND 5 C loroform ND 5 1,1,1-Trichloroethane ND 5 Carbon Tetrachloride ND 5 1,2-Dichloroethane ND 5 Trichloroethene ND 5 1 1 2-Dichloropropane ND 5 D1bromomethane ND 5 Bromodichloromethane ND 5 2-Chloroethyl vinylether ND 5 trans-1,3-Dichloropropene ND 5 ci~-1,3-Dichloro~ropene ND 5 1,1,2-Trichloroe hane ND 5 Tetrachloroethene ND 5 i,3-0ichloropro~ane ND 5 1 1 1,1,2-Tetrach oroethane ND 5 D1bromochloromethane ND 5 Ethylene Dibromide ND 5 Chlorobenzene ND 5 Bromoform ND 5 lhl,2,2-Tetrachloroethane ND 5 C lorotoluene ND 5 1,3-Dichlorobenzene ND 5 1,4-Dichlorobenzene ND 5 1,2-Dichlorobenzene ND 5 Benzylchloride ND 5 SURROGATE PARAMETER % RECOVERY QC LIMIT ---------------------------- - - - - Bromofluorobenzene 94 60-140 MDL: Method Detection Limit CKY INC., ANALYTICAL lABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618·0818 I I IENT: Ogden Environmental OJECT: Brandywine METHOD: EPA 8010 MATRIX: SOIL CKY QUALITY CONTROL DATA MS/MSD ANALYSIS I MOISTURE: 24.3 BATCH NO.: 968085 DATE RECEIVED: 02/19/96 IAMPLE ID: BWBS01S02D71 DATE EXTRACTED: NA ONTROL NO.: 8085-02 DATE ANALYZED: 02/21/96 ACCESSION: 968085 IRAMETER SMPL RSLT SPIKE AMT MS RSLT MS SPIKE AMT MSD RSLT MSD RPD QC LIMIT RPD LIMIT ug/kg) (ug/kg) (ug/kg) % REC (Ug/kg) (Ug/kg) % REC % % % 1, 1-Dichloroethene ND 330.00 298.00 90 330.00 278.00 84 7 60-140 40 ichloroethene ND 330.00 277.00 84 330.00 274.00 83 1 60-140 40 lorobenzene ND 330.00 246.00 75 330.00 236.00 71 4 60-140 40 I =========================================================.========================================================================= SPIKE AMT MS RSLT MS SPIKE AMT MSD RSLT MSD QC LIMIT SURROGATE PARAMETER (ug/kg) (ug/kg) % REC (ug/kg) (ug/kg) % REC % 1·omof l uorobenzene I I I I I 1. 330.00 336.00 102 330.00 217.00 66 60-140 I I I I I CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I IENT: Ogden Environmental OJECT: Brandywine METHOD: EPA 8D1 D MOISTURE: NA CKY QUALITY CONTROL DATA LCS/LCD ANALYSIS ITRIX: SOIL BATCH NO.: IMPLE ID: NTROL NO.: ACCESSION: IRAMETER 96B085 LCS1S/LCS1SD VAL617L/C 96B085 BLNK RSLT ug/kg) SPIKE AMT BS RSLT BS ug/kg) (ug/kg) % REC SPIKE AMT ug/kg) DATE RECEIVED: NA DATE EXTRACTED: NA DATE ANALYZED: 02/19/96 BSD RSLT BSD RPD ug/kg) % REC % QC LIMIT RPD LIMIT 1·Dichloroethene ND 100.00 111.00 111 100.00 109.00 109 2 70·125 40 ichloroethene ND 100.00 113.00 113 100.00 112.00 112 1 70·125 40 lorobenzene ND 100.00 111.00 111 100.00 114.00 114 3 70-125 40 SPIKE AMT BS RSLT BS SPIKE AMT BSD RSLT BSD QC LIMIT SURROGATE PARAMETER (ug/kg) (ug/kg) % REC (ug/kg) (ug/kg) % REC % - omofluorobenzene 250.00 229.00 91 250.00 238.00 95 60-140 I I I I I I I I I I CKY INC., ANALYTICAL lABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618·8889 Fax: 13 lOl 61S·•'818 I I IENT: Ogden Environmental OJECT: Brandywine. METHOD: EPA 8010 MOISTURE: NA CKY QUALITY CONTROL DATA LCS/LCD ANALYSIS TRIX: SOIL BATCH NO.: I. MPLE ID: NTROL NO.: ACCESSION: IRAMETER 968085 LCS2S/LCS2SD VAL617L2/C2 968085 BLNK RSLT ug/kg) SPIKE AMT BS RSLT BS ug/kg) (ug/kg) % REC SPIKE AMT ug/kg) DATE RECEIVED: NA DATE EXTRACTED: NA DATE ANALYZED: 02/21/96 BSD RSLT BSD RPO ug/kg) % REC % QC LIMIT RPO LIMIT 1, l·Dichloroethene ND 100.00 113. so 114 100.00 91.50 92 21 70· 125 40 lichloroethene ND 100.00 104.00 104 100.00 97.50 98 6 70·125 40 lorobenzene ND 100.00 101.00 101 100.00 94.00 94 7 70· 125 40 SPIKE AMT BS RSLT BS SPIKE AMT BSD RSLT BSD QC LIMIT SURROGATE PARAMETER (ug/kg) (ug/kg) % REC (ug/kg) (ug/kg) % REC % omofluorobenzene 250.00 209.00 84 250.00 172.00 69 60-140 I I I I I I I I I I CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I I I EPA METHOD 8020 BTEX CLIENT: Ogden Environmental DATE COLLECTED: 02/17/96 PROJECT: Brandywine DATE RECEIVED: 02/19/96 BATCH NO.: 96B085 DATE EXTRACTED: NA SAMPLE ID: BWBSOlSOlDlO.O DATE ANALYZED: 02/21/96 CONTROL NO.: B085-01 MATRIX: SOIL MOISTURE: 8.7 DILUTION FACTOR: 1 RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Benzene ND 5.48 Toluene ND 5.48 Ethylbenzene ND 5.48 Total Xylenes ND 16.4 SURROGATE PARAMETER % RECOVERY QC LIMIT ---------------------------- - - -- Bromofluorobenzene 65 60-140 MDL: Method Detection Limit I~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I I I I EPA METHOD 8020 BTEX CLIENT: Ogden Environmental DATE COLLECTED: 02/17/96 PROJECT: Brandywine DATE RECEIVED: 02/19/96 BATCH NO.: 96B085 DATE EXTRACTED: NA SAMPLE ID: BWBS01S02D71 DATE ANALYZED: 02/20/96 CONTROL NO.: B085-02 MATRIX: SOIL MOISTURE: 24.3 DILUTION FACTOR: 1 RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Benzene ND 6.61 Toluene ND 6.61 Ethylbenzene ND 6.61 Total Xylenes ND 19.8 SURROGATE PARAMETER % RECOVERY QC LIMIT ---------------------------- - - -- Bromofluorobenzene 45+ 60-140 MDL: Method Detection Limit Out of QC limits, sample was reanalyzed on 02/22/96. CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I I EPA METHOD 8020 BTEX CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO. : MOISTURE: Ogden Environmental Brandywine 96B085 BWBS01S02D71 B085-02R 24.3 DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: 02/17/96 02/19/96 NA 02/22/96 SOIL 1 RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Benzene ND 6.61 Toluene ND 6.61 Ethylbenzene ND 6.61 Total Xylenes ND 19.8 SURROGATE PARAMETER % RECOVERY QC LIMIT --------- --------- Bromofluorobenzene 43+ 60-140 MDL: Method Detection Limit Out of QC limits on reanalysis run I ~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I I I EPA METHOD 8020 BTEX CLIENT: Ogden Environmental DATE COLLECTED: 02/17/96 PROJECT: Brandywine DATE RECEIVED: 02/19/96 BATCH NO.: 96B085 DATE EXTRACTED: NA SAMPLE ID: BWBS02S01Dll.O DATE ANALYZED: 02/20/96 CONTROL NO.: B085-03 MATRIX: SOIL MOISTURE: 14.0 DILUTION FACTOR: 1 RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Benzene ND 5.81 Toluene ND 5.81 Ethylbenzene ND 5.81 Total Xylenes ND 17.4 SURROGATE PARAMETER % RECOVERY QC LIMIT ---------------------------- - - - - Bromofluorobenzene 65 60-140 MDL: Method Detection Limit I G\, CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (3 l!)! 6: ~-11818 I I I I I I I I I I I I I I I I I I EPA METHOD 8020 BTEX CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO . : MOISTURE: Ogden Environmental Brandywine 96B085 BWBS02S02D56.0 B085-04 24.1 DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: 02/17/96 02/19/96 NA 02/20/96 SOIL 1 RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Benzene ND 6.59 Toluene ND 6.59 Ethylbenzene ND 6.59 Total Xylenes ND 19.8 SURROGATE PARAMETER % RECOVERY QC LIMIT ---------------------------- - - - - Bromofluorobenzene 66 60-140 MDL: Method Detection Limit I Giy CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave.', Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I I I EPA METHOD 8020 BTEX CLIENT: Ogden Environmental DATE COLLECTED: 02/18/96 PROJECT: Brandywine DATE RECEIVED: 02/19/96 BATCH NO.: 96B085 DATE EXTRACTED: NA SAMPLE ID: BWBS03S01D10.5 DATE ANALYZED: 02/20/96 CONTROL NO.: B085-05 MATRIX: SOIL MOISTURE: 11.9 DILUTION FACTOR: 1 RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Benzene ND 5. 68 Toluene ND 5.68 Ethylbenzene ND 5.68 Total Xylenes ND 17 SURROGATE PARAMETER % RECOVERY QC LIMIT --------- --------- Bromofluorobenzene 65 60-140 MDL: Method Detection Limit I G\, CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave., Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618·0818 I I I I I I I I I I I I I I I I I I EPA METHOD 8020 BTEX CLIENT: Ogden Environmental DATE COLLECTED: 02/18/96 PROJECT: Brandywine DATE RECEIVED: 02/19/96 BATCH NO. : 96B085 DATE EXTRACTED: NA SAMPLE ID: BWBS03S02D66.5 DATE ANALYZED: 02/20/96 CONTROL NO.: B085-06 MATRIX: SOIL MOISTURE: 22.7 DILUTION FACTOR: 1 RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Benzene ND 6.47 Toluene ND 6.47 Ethylbenzene ND 6.47 Total Xylenes ND 19.4 SURROGATE PARAMETER % RECOVERY QC LIMIT ------------------------------ - - Bromofluorobenzene 52+ 60-140 MDL: Method Detection Limit Out of QC limits, sample was reanalyzed on 02/22/96. I~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I I I EPA METHOD 8020 BTEX CLIENT: Ogden Environmental DATE COLLECTED: 02/18/96 PROJECT: Brandywine DATE RECEIVED: 02/19/96 BATCH NO.: 96B085 DATE EXTRACTED: NA SAMPLE ID: BWBS03S02D66.5 DATE ANALYZED: 02/22/96 CONTROL NO.: B085-06R MATRIX: SOIL MOISTURE: 22.7 DILUTION FACTOR: 1 RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Benzene ND 6.47 Toluene ND 6.47 Ethylbenzene ND 6.47 Total Xylenes ND 19.4 SURROGATE PARAMETER % RECOVERY QC LIMIT ------------------------------ - - Bromofluorobenzene 45+ 60-140 MDL: Method Detection Limit Out of QC limits on reanalysis run I ~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I I I· I EPA METHOD 8020 BTEX CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO . : MOISTURE: Ogden Environmental Brandywine 96B085 BWBS03S03D75.5 B085-07 19.7 DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: 02/18/96 02/19/96 NA 02/20/96 SOIL 1 RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Benzene ND 6.23 Toluene ND 6.23 Ethylbenzene ND 6.23 Total Xylenes ND 18.7 SURROGATE PARAMETER % RECOVERY QC LIMIT ---------------------------- - - - - Bromofluorobenzene 67 60-140 MDL: Method Detection Limit CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: 131 Ol 61 ~-os 1a I I I I I I I I I I I I I I I I I I EPA METHOD 8020 BTEX CLIENT: PROJECT: BATCH NO.:· SAMPLE ID: CONTROL NO . : MOISTURE: PARAMETERS ---------- Benzene Toluene Ethylbenzene Total Xylenes Ogden Environmental Brandywine 96B085 MBLKlS VAL617B NA SURROGATE PARAMETER ------------------ Bromofluorobenzene MDL: Method Detection Limit DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: RESULTS NA NA NA 02/19/96 SOIL 1 MDL ug/kg) (ug/kg) -------------- ND 5 ND 5 ND 5 ND 15 RECOVERY QC LIMIT ------------ - 77 60-140 I G\, CKY INC., ANALYTICAL lABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I I I EPA METHOD 8020 BTEX CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO . : MOISTURE: Ogden Environmental Brandywine 96B085 MBLK2S VAL617B3 NA DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: NA NA NA 02/21/96 SOIL 1 RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Benzene ND 5 Toluene ND 5 Ethylbenzene ND 5 Total Xylenes ND 15 SURROGATE PARAMETER % RECOVERY QC LIMIT ---------------------------- - - - - Bromofluorobenzene 65 60-140 MDL: Method Detection Limit CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I IENT: Ogden Environmental OJECT: Brandywine METHOD: EPA 8020 MOISTURE: 24.3 CKY QUALITY CONTROL DATA MS/MSD ANALYSIS TRIX: SOIL BATCH NO.: 966085 DATE RECEIVED: 02/19/96 I MPLE ID: BWBS01S02D71 DATE EXTRACTED: NA NTROL NO.: B085-02 DATE ANALYZED: 02/21/96 ACCESSION: 96B085 IRAMETER SMPL RSLT SPIKE AMT MS RSLT MS SPIKE AMT MSD RSLT MSD RPO ug/kg) (ug/kg) (ug/kg) % REC (ug/kg) (ug/kg) % REC % Benzene l luene . hylbenzene tal Xylenes ND ND ND ND 330.00 330.00 330.00 991.00 240.00 73 221.00 67 223.00 68 614.00 62 330.00 238.00 72 1 330.00 221.00 67 0 330.00 221.00 67 1 991.00 620.00 63 1 QC LIMIT RPO LIMIT 60-140 40 60-140 40 60-140 40 60-140 40 SURROGATE PARAMETER 1-----------------omofluorobenzene I I I I I I I I I SPIKE AMT MS RSLT MS SPIKE AMT MSD RSLT MSD QC LIMIT ug/kg) (ug/kg) % REC (ug/kg) (ug/kg) % REC % 330.00 221.00 67 330.00 217.00 66 60-140 I ,~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: i310l 618-0818 I I IENT: Ogden Environmental OJECT: Brandywine METHOD: EPA 8020 MOISTURE: NA CKY QUALITY CONTROL DATA LCS/LCD ANALYSIS TRIX: SOIL BATCH NO.: I MPLE ID: NTROL NO.: ACCESSION: IRAMETER Benzene l luene hylbenzene tal Xylenes 968085 LCS1S/LCS1SD VAL617L/C 968085 BLNK RSLT ug/kg) ND ND ND ND SPIKE AMT BS RSLT BS ug/kg) (ug/kg) % REC 100.00 85.00 85 100.00 87.00 87 100.00 97.00 97 300.00 233.00 78 SPIKE AMT ug/kg) 100.00 100.00 100.00 300.00 DATE RECEIVED: NA DATE EXTRACTED: NA DATE ANALYZED: 02/19/96 BSD RSLT BSD RPD ug/kg) % REC % 86.00 86 88.00 88 98.00 98 237.00 79 QC LIMIT RPD LIMIT 70-125 40 70-125 40 70-125 40 70-125 40 I I I I I I I I I I ,~ SPIKE AMT BS RSLT BS SPIKE AMT BSD RSLT BSD QC LIMIT ug/kg) (ug/kg) % REC (ug/kg) (ug/kg) % REC % 250.00 244.00 98 250.00 255.00 102 60-140 CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I IENT: Ogden Environmental OJECT: Brandywine METHOD: EPA 8020 MOISTURE: NA CKY QUALITY CONTROL DATA LCS/LCD ANALYSIS ITRIX: SOIL BATCH NO.: 96B085 DATE RECEIVED: NA IMPLE ID: LCS2S/LCS2SD DATE EXTRACTED: NA NTROL NO.: VAL617L2/C2 DATE ANALYZED: 02/21/96 ACCESSION: 968085 IRAMETER BLNK RSLT SPIKE AMT BS RSLT BS SPIKE AMT BSD RSLT BSD RPD QC LIMIT RPD LIMIT Cug/kg) Cug/kg) Cug/kg) % REC (ug/kg) (ug/kg) % REC % % % Benzene ND 100.00 84.00 84 100.00 80.00 80 5 70· 125 40llueneND100.00 84.50 84 100.00 78.00 78 8 70· 125 40 hylbenzene ND 100.00 93.00 93 100.00 85.00 85 9 70-125 40 tal Xylenes ND 300.00 223.00 74 300.00 216.00 72 3 70-125 40 I I I I I I I I I I ,~ SPIKE AMT BS RSLT BS SPIKE AMT BSD RSLT BSD QC LIMIT ug/kg) (ug/kg) % REC (ug/kg) (ug/kg) % REC % 250.00 227.00 91 250.00 186.00 74 60-140 CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (31 Oi b I 8-11818 I I I I I I I I I I I I I I I I I 1----- 1 STERLING Analytical Laboratory CKY Inc. Analytical Laboratories 630 Maple Avenue Torrance, CA 90503 Attn: Cecilia Chavez Job No.: 0691081.00 Project No.: 95B085 Project Name: Ogden Folder No.: 4307 LABORATORY REPORT February 26, 1996 Page 1 of 1 Samples: Seven (7) soil samples from 95B085-0dgen, collected on 02/17/96 and 02/18/96 and received on 02/20/96. Sample ID 96B085-01 96B085-02 96B085-03 96B085-04 96B085-05 96B085-06 96B085-07 TOC Walkley Black) Reporting Limit Date Analyzed c43-07. rep----------·---- 2860 Walnut Avenue Long Beach, CA 90806-1 834 0.201 0.354 0.078 0.059 0.171 0.038 0.032 0.010 02/23/96 1800) 366-9324 • 1310) 595-9324 310) 595-6709 FAX I I I I I I I I I I I I I I I I I I 1 STERLING Analytical Laboratory LAB ID SYMBOL 4307-7 Quality Assurance Addendum Report Page 1 of 1 TEST TOC UNITS Notes: QA/QC Results Sample Dup. RPD(%) 0.032 0.027 17 Note that Matrix Spikes are not project specific. Therefore, spike information shown on this report may not be from the same project; however, they were anaiyzed in the same analytical batch. Definitions: Spike: A sample from the analytical batch which has been spiked with the parameter(s) of interest at a known concentration and taken through the same preparation and analysis as the samples. Spike Duplicate: A duplicate of the spiked sample, taken from a separate aliquot of the sample. RPD: Mean: Relative Percent Difference between a Spike and a Spike Duplicate (or a sample and sample duplicate). RPD = [(Spike-Spk. Dup.)/Mean] * 100 Where the mean is the average spike recovery of the matrix spike and the matrix spike duplicate. The average sample results, from both samples and sample duplicates. Control limits are calculated by Sterling Analytical Laboratory for internal use from existing spike ~ata. Control limits are found by calculating three standard deviations above and below the mean of the population. C4307.qa L/~7 I I CHAIN OF CUSTODY RECORDCLIENT NA~E: CK~ .INC... REQUEST FOR ANALYSJS 4~ CK Y incorporated AD~REss: &3o /\1Jtf'lF" AVE DATE: 2.-1, '"'1b _ Analyticu/ Laboratories I Ilf?B.A:N: t1: 41 . s oso-3 PAGE--i-OF I h30 Maple Ave, forrance, Calif. 90503 PHONE NO. 3/Q-€/ g. ~ FAX NO. 'Sf 6 r' /'fr 9"8'/ f Tel: 310·618-8889 PRdlJECTNAME: CJr/3 ~ L ~.1>~ . Fax: 310-618-0818 SEND REPORT TO: C.~I U A CH-A V (;' "'2._ , I TURN AROUND TIME ANALYSES REQUIRED SAMPLER NAME/SIGNATURE NORMAL ~ I V) I RUSH '" ~ ..,. I{) " iii ~ D ~ g N N Q) D <D ~ ' ~ 0 0 0 ~ ' i SAMPLE SAMPLING PRESER-CONTAINER SAMPLE DESCRIPTION a:i fiS 0 ! ~ ~ (\ J '<t "- I NUMBER DATE/TIME ~ ~ al N (\j <( VATIVE SIZE/TYPE WATER SOIL OTHER '<t co co u I q GB og.s -1' I 2-/ 11 / 'i' '1 f•Jo ';J(.£ lt-~~n-9-X )( I / 1>31 ,,, z, I -Ol-I I -~..3 ! I l3trJ 1 I -() Lf J llftoI c:; I -01' 2-/19"/e;C /2.30i I ~o, I l3SJ I -07 rJ l't2'7 ,:I• ,., -1 I ,: I:, , .. I I I i I I I I COM~ENTS: I J - iff,/t;~" F}ef~ived ~y~Signat_urev i!t!o~~ Relinquished by: (Signature) Date: Received by: (Signature) Date: JI Confp1any: Time: Company: {I o' Time: Company: Time: Company: Time: I u{-< 2.rN fk ~E~J,,fj/(;-J.j.J?, c;J..:""'IIV .' 1- Storade/Disposal of Samples: Sample will be stored at CKY for 30 days at no charge and at $10/sampie/month thereafter. Disposal of sample by the Laboratory will be charged at $10/sample, i I 1. 3 f j b 7 qb /3oRr L-~ ' I I CHAIN OF CUSTODY RECORD CLIENT 1A. ~ · · 0. NAME: ' _p,..) _Aft.£1/£ £3 d.p£.,; REQUEST FOR v.NALYSIS ~ CK Y f•~,poro<,d ADD~ESS: 5S'./O. Mo~#Al~d5£ :D,,,,_ Analytical Laboratories I ~u& ... 1 "1//~/" -A ~ A "f 2.J ~ J DATE: 2.. j } 8 'J:b , 630 Maple Ave. IPAGE_}_ ~F J _ · l'orrance, Calif. 90503 I PHONE NO. ~i'l'f .+SP. -9,..'ld FAX NO. ~ 11 / .4-~4 -~'7_$ . . " . ~ ~ re1, 310-618-8889 Fax: 310·618-0818 PROJ~CT NAME( L ~~.,;, \,) J.. , /.IL'~ F , SENDI REPORT TO: -r?.;. • ,r U.AAIJ),~ -,_ TURN AROUND TIME ~ ANALYSES REQUIRED ' SAMPLER NAME/ZTURE ~ . ·~ r<.. NORMAL w-~ '' lh,<l ~i~J --~v>-> UI RUSH D I I I ..,. ll') ] j ,,.. I (\ j ! ~ <J'' ~ ll') ~ SAMPLE SAMPLING jPRESER-CONTAINER SAMPLE DESCRIPTION· -co 2 ..... ~ <::. Q, . I :;: ~ ~ : NUMBER DATE/TIME VATIVE SIZE/TYPE WATER SOIL OTHER () ~ ~"'"" r~~o/S4/D/D,C 2}11e> t>flo JC-)( )( ll.i~1>JS02;:, ':/-/ 2.11~/L>IS lit' J<. )( 1vJ~2SAJ DJJ. o 2h-?-b ).ID 5 X )<. X J __, ,j),:1,. J U;J/l'll'~fl''7_ f: 111'1...,, 1.J.10 ){ X X J,,j/5b~t>I P )"• ,;' 'Z}l&t!J )2...ae> ')( )<. X 1k.>8Jo:J~~ ~fDJ,~ ; 2hf>~ ,;6'J )<. X )( JI~;,~~~ n 7S.E jJJg.e, )h:J-X )( X I ~- I I I II . j I I . I I I COMMENTS: ' r.=2,'c-~ 1-, - i..,,. .. ~ignature) a Yii \ q I.,.,. ~~) ~9-*-Oat~ . Received by: (Signature) 2.Da~e/t-'?'6' ~.., ~ ::1 -I -'1(, CompapY 'rime:'· eo~v;,,,~ TW1: &>i:npany: -·· Time: Company: Time: otb~,..:J :J.,} ·, ~;. ~J--.,..._ 11 :rr e,,ft.t I /Jr-' / .,/ .,-... ~ , -. I' StoragJ/Oisposal of Samples: Sample will be stored at CKY for 30 days at no charge and at $10/sample/month t~reafter. Disposal of sample by the Laboratory '!"(ill be charged at $10/sarnple. i t 1 f I --~---------------- n 2r i 0 1 I CONTROL NO. 9680~ CLIENT (Jl)·~e-N PROJECT ~,., ~13) \/ h> Iti"t: SAMPLE TRANSPORTATION TO CKY LABORATORY: PICKED-UP BY CKY COURIER DElltVERED BY CLIENT ;'° .. SHIPPED/AIRBILL NO A"M ---f' M b €'l.J V E1l>, #4/D SAMPLE BATCH PACKAGING/SEALING UPON RECEIPT: co,iJTAINER: J INSIDE TEMPERATURE: i'cooLER PACKAGING . · .TYPE I BOX INSULATION: i OTHER: ICE/COOLANT: Bt.,.UE I PACKING MATERIAL: N1rH'1i" SAMPLE RECEIPT FORM DATE 02-lq -96 TIME II·. 3r HI RECIPIENT ~. Tl AN-k u., BY ON(DATE) AT(TIME) FROM(SITE/CO.) COMMENTS Ql)Lf, ~ ,~~(-cl{J '1 NO CONTAINER /INTACT DAMAGED NOT SEALED i"sEALED ci.,d C CUSTODY SEAL /OTHER SEAL LOCATION NUMBER SUFFICIENCY ,.......INTACT DAMAGED ~' ac1l t<fl. :-( 1.P-NAME: %-'-(?-Cc/'"1:..... t DATE: J.. TIME: i !SAMPLE DOCUMENTATION/CHAIN-OF-CUSTODY(COC) I . NONE I /HANDCARRIED I ENCLOSED I FAXED· SEALED fii JI> w Q 3: i- 1 t J I'°' w ... , g f 00 00 0 w w ... , g 00 b 00 ... 00 SAMPLE LOG-IN: . CRITERIA COMMENTS SAMPLE CUSTODY SEAL EVERY' SAMPLE N~C CONTAINER TYPE/MATERIAL APPROPRIATE "'~ SAMPLE AMOUNT ENOUGH SAMPLE PRESERVATION/HOLDING TIME SUFFICIENT HEADSPACE/BUBBLES ZERO/NONE -,- SAMPLE LABEL INFORMATION SUFFICIENT "~ . ~ CHAIN-OF-CUSTODY INFORMATION SUFFICIENT 4,.., SAMPLE INFO.: SAMPLE ID -·· DATE -TIME -I SIGNATURE -I INDIVIDUAL SAMPLE CONTAINER: 'NONE PLASTIC BAG I CAN· SAMPll.E NUMBER CLIENT ID DISCREPANCY I .MA,,' -~~t& I~ ~ (,r~~W1:.1"- I W1 D f:I tJ'U•T ~IU/J I ...,, A. -.M!-~I o/ I I _, AWA<ot~c> I 1>102 Nl'1"' ~ fl,~ 1!£{..,b t~ ~ I W A-:sf/l c;t, I 5: t, I 'J}} 0 , (I ___. I I .. / ----- I I / __...- V 4 . ---- I / __.,.- I I J I /"") _ I I J I DATE DISCREPANCY / ANALYSES ,. PRESERVATIVE I CONTAINER ' OTHER(SPECIFY): I SEALED rl /I • 1 ACTION pvil,L. f .. hff!,~ / tJ.,A'.,1-0.,7] • n.l'I· V _,.., -// VP . (,,(;(a...J .[fa,J ·~ TIME I I I I I I I I I I I I I I I I I I 1 Date: 02-22-1996 CKY Batch No.: 96B042 Attn: Don Barrie Ogden Environmental 5510 Morehouse Drive San Diego, CA 92121 Subject: Laboratory Report Project: Chula Vista CK Y incorporated Analytical Laboratories Enclosed is the Laboratory report for samples received on 02/12/96. The samples were received in coolers with ice and intact; the chain-of-custody forms were properly filled out. The data reported include : Sample ID Control No. -------------------- BWB505S01D10.0 B042-01 BWB505S04D85.5 BWB505S05D91 BWB504S01D26.5 BWB504S02D76.5 BWB504S03D86.0 B042-02 B042-03 B042-04 B042-05 B042-06 Matrix Soil Soil Soil Soil Soil Soil Analysis -------- EPA EPA TOC EPA EPA TOC EPA EPA TOC EPA EPA TOC EPA EPA TOC EPA EPA TOC 8010 8020 8010 8020 8010 8020 8010 8020 8010 8020 8010 8020 The results are summarized on the following pages. Please feel free to call if you have any questions concerning these results. Sincerely yours, R~ --------~------ Kam Y. Pang~ Ph.D. Laboratory uirector P.S. -All analyses requested for the above referenced project have been completed. Therefore, unless instructed, the remaining Qortions of tne samples will be disposed after fifteen (15) days rrom the date of this report. 630 Maple Ave., Torrance, Calif. 90503 • Telephone 310-618-8889 • Fax: 310-618-0818 I I 1· I I I I I I I I I I I I I I 1~- EPA METHOD 8010 HALOGENATED VOLATILE ORGANICS CLIENT: Oqden Environmental DATE COLLECTED: 02/10/96 PROJECT: Cfiula Vista DATE RECEIVED: 02/12/96 BATCH NO.: 96B042 DATE EXTRACTED: NA SAMPLE ID: BWB505S01D10.0 DATE ANALYZED: 02/12/96 CONTROL NO.: B042-01 MATRIX: SOIL % MOISTURE: 8.9 DILUTION FACTOR: 1 =============================----=====--======-===================== RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Dichlorodifluoromethane ND 27.4 Chloromethane ND 27.4 Vinyl Chloride ND 27.4 Bromomethane ND 27.4 Chloroethane ND 27.4 Trichlorofluoromethane ND 5.49 1,1-Dichloroethene ND 5.49 Meth1lene Chloride ND 27.4 cis-,2-Dichloroethene ND 5.49 trans-ln2-Dichloroethene ND 5.49 lnl-Dic loroethane ND 5.49 C loroform ND 5.49 1,101-Trichloroethane ND 5.49 Car on Tetrachloride ND 5.49 1,2-Dichloroethane ND 5.49 Trichloroethene ND 5.49 1,2-Dichloropropane ND 5.49 Dibromomethane ND 5.49 Bromodichloromethane ND 5.49 2-Chloroethyl vinylether ND 5.49 trans-1,3-Dichloropropene ND 5.49 cis-1,3-Dichlorogropene ND 5.49 1,1,2-Trichloroe hane ND 5.49 Tetrachloroethene ND 5.49 1,3-Dichloropro~ane ND 5.49 1,1,1,2-Tetrach oroethane ND 5.49 Dibromochloromethane ND 5.49 Ethylene Dibromide ND 5.49 Chlorobenzene ND 5.49 Bromoform ND 5.49 lnl,2,2-Tetrachloroethane ND 5.49 C lorotoluene ND 5.49 1,3-Dichlorobenzene ND 5.49 1,4-Dichlorobenzene ND 5.49 1,2-Dichlorobenzene ND 5.49 Benzylchloride ND 5.49 SURROGATE PARAMETER % RECOVERY QC LIMIT ---------------------------- - - - - Bromofluorobenzene 108 60-140 MDL: Method Detection Limit CKY INC., ANALYTICAL IABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (3l0) 618-0818 I I I I I I I I I I I I I I I I I EPA METHOD 8010 HALOGENATED VOLATILE ORGANICS CLIENT: PROJECT: Ogden Environmental DATE COLLECTED~--02/10/.96 Cfiula Vista DATE RECEIVED: 02/12/96 BATCH NO.: 96B042 DATE EXTRACTED: NA SAMPLE ID: CONTROL NO . : MOISTURE: BWB505S04D85.5 DATE ANALYZED: 02/12/96 B042-02 MATRIX: sotL 23.1 DILUTION FACTOR: 1 RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Dichlorodifluoromethane ND 32.5 Chloromethane ND 32·. 5 Vinyl Chloride ND 32.5 Bromomethane ND 32.5 Chloroethane ND 32.5 Trichlorofluoromethane ND 6.5 1,1-Dichloroeth~ne ND 6.5 Meth1lene Chloride ND 32.5 cis-,2-Dichloroethene ND 6.5 trans-lh2-Dichloroethene ND 6.5 lhl-Dic loroethane ND 6.5 C loroform ND 6.5 1,1,1-Trichloroethane ND 6.5 Carbon Tetrachloride ND 6.5 1,2-Dichloroethane ND 6.5 Trichloroethene ND 6.5 1,2-Dichloropropane ND 6.5 D1bromomethane ND 6.5 Bromodichloromethane ND 6.5 2-Chloroethyl vinylether ND 6.5 trans-1,3-Dichloropropene ND 6.5 cis-1,3-Dichloro~ropene ND 6.5 1,1,2-Trichloroe hane ND 6.5 Tetrachloroethene ND 6.5 1,3-Dichloropro~ane ND 6.5 1,1,l,2-Tetrach oroethane ND 6.5 D1bromochloromethane ND 6.5 Ethylene Dibromide ND 6.5 Chlorobenzene ND 6.5 Bromoform ND 6.5 lhl,2,2-Tetrachloroethane ND 6.5 C lorotoluene ND 6.5 1,3-Dichlorobenzene ND 6.5 1,4-Dichlorobenzene ND 6.5 1,2-Dichlorobenzene ND 6.5 Benzylchloride ND 6.5 SURROGATE PARAMETER % RECOVERY QC LIMIT ---------------------------- - - - - Bromofluorobenzene 108 60-140 MDL: Method Detection Limit 1---- I G\, CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .• Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO. : MOISTURE: EPA METHOD 8010 HALOGENATED VOLATILE ORGANICS Oqden Environmental DATE COLLECTED: Cfiula Vista DATE RECEIVED: 96B042 DATE EXTRACTED: BWB505SOSD91 DATE ANALYZED: B042-03 MATRIX: 20.1 DILUTION FACTOR: 02/10/96 02/12/96 NA 02/12/96 SOIL 1 =============================-========-============================= RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Dichlorodifluoromethane ND 31. 3 Chloromethane ND 31. 3 Vinyl Chloride ND 31.3 Bromomethane ND 31. 3 Chloroethane ND 31. 3 Trichlorofluoromethane ND 6.26 1,1-Dichloroeth~ne ND 6.26 Meth1lene Chloride ND 31. 3 cis-,2-Dichloroethene ND 6.26 trans-lh2-Dichloroethene ND 6.26 lhl-Dic loroethane ND 6.26 C loroform ND 6.26 l,lbl-Trichloroethane ND 6.26 Car on Tetrachloride ND 6.26 1,2-Dichloroethane ND 6.26 Trichloroethene ND 6.26 1 1 2-Dichloropropane ND 6.26 D1bromomethane ND 6.26 Bromodichloromethane ND 6.26 2-Chloroethyl vinylether ND 6.26 trans-1,3-Dichloropropene ND 6.26 cis-1,3-Dichloro~ropene ND 6.26 1,1,2-Trichloroe hane ND 6.26 Tetrachloroethene ND 6.26 1,3-Dichloropro~ane . ND 6.26 1,1,1,2-Tetrach oroethane ND 6.26 D1bromochl.oromethane ND 6.26 Ethylene Dibromide ND 6.26 Chlorobenzene ND 6.26 Bromoform ND 6.26 lhl,2,2-Tetrachloroethane ND 6.26 C lorotoluene ND 6.26 1,3-Dichlorobenzene ND 6.26 1,4-Dichlorobenzene ND 6.26 1,2-Dichlorobenzene ND 6.26 Benzylchloride ND 6.26 SURROGATE PARAMETER % RECOVERY QC LIMIT ---------------------------- - - - - Bromofluorobenzene 66 60-140 MDL: Method Detection Limit I · ~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I EPA METHOD 8010 HALOGENATED VOLATILE ORGANICS CLIENT: PROJECT: Ogden E~vironmental DATE COLLECTED~--02/11/.96 Cfiula Vista DATE RECEIVED: 02/12/96 BATCH NO.: 96B042 DATE EXTRACTED: NA BWB504S01D26.5 DATE ANALYZED: 02/12/96SAMPLEID: CONTROL NO. : MOISTURE: B042-04 MATRIX: SOIL 6.6 DILUTION FACTOR: 1 RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Dichlorodifluoromethane ND 26.8 Chloromethane ND 26.8 Vinyl Chloride ND 26.8 Bromomethane ND 26.8 Chloroethane ND 26.8 Trichlorofluoromethane ND 5.35 1,1-Dichloroethene ND 5.35 Meth1lene Chloride ND 26.8 cis-,2-Dichloroethene ND 5.35 trans-lh2-Dichloroethene ND 5.35 lhl-Dic loroethane ND 5.35 C loroform ND 5.35 1,161-Trichloroethane ND 5.35 Car on Tetrachloride ND 5.35 1,2-Dichloroethane ND .5.35 Trichloroethene ND 5.35 1,2-Dichloropropane ND 5.35 D1bromomethane ND 5.35 Bromodichloromethane ND 5.35 2-Chloroethyl v1nylether ND 5.35 trans-1,3-Dichloropropene ND 5.35 cis-1,3-Dichloro~ropene · ND 5.35 1,1,2-Trichloroe hane ND 5.35 Tetrachloroethene ND 5.35 1,3-Dichloropro~ane ND 5.35 1,1,1,2-Tetrach oroethane ND 5.35 D1bromochloromethane ND 5.35 Ethylene Dibromide ND 5.35 Chlorobenzene ND 5.35 Bromoform ND 5.35 lhl,2,2-Tetrachloroethane ND 5.35 C lorotoluene ND 5.35 1,3-Dichlorobenzene ND 5.35 1,4-Dichlorobenzene ND 5.35 1,2-Dichlorobenzene ND 5.35 Benzylchloride ND 5.35 SURROGATE PARAMETER % RECOVERY QC LIMIT ---------------------------- - - - - Bromofluorobenzene 104 60-140 I MDL: Method Detection Limit I I I 1~---- I ~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818. I I I I I I I I I I I I I I I I I EPA METHOD 8010 HALOGENATED VOLATILE ORGANICS CLIENT: Ogden Environmental DATE COLLECTED: 02/11/96 PROJECT: Cfiula Vista DATE RECEIVED: 02/12/96 BATCH NO.: 96B042 DATE EXTRACTED: NA SAMPLE ID: BWB504S02D76.5 DATE ANALYZED: 02/13/96 CONTROL NO.: B042-05 MATRIX: SOIL MOISTURE: 21.9 DILUTION FACTOR: 1 ============-----===---======---======-============================= RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Dichlorodifluoromethane ND 32 Chloromethane ND 32 Vinyl Chloride ND 32 Bromomethane ND 32 Chloroethane ND 32 Trichlorofluoromethane ND 6.4 1,1-Dichloroeth~ne ND 6.4 Meth1lene Chloride ND 32 cis-,2-Dichloroethene ND 6.4 trans-lh2-Dichloroethene ND 6.4 lhl-Dic loroethane ND 6.4 C loroform ND 6.4 1,161-Trichloroethane ND 6.4 Car on Tetrachloride ND 6.4 1,2-Dichloroethane ND 6.4 Trichloroethene ND 6.4 1,2-Dichloropropane ND 6.4 Dibromomethane ND 6.4 Bromodichloromethane ND 6.4 2-Chloroethyl vinylether ND 6.4 trans-1,3-Dichloropropene ND 6.4 cis-1,3-Dichlorogropene ND 6.4 1,1,2-Trichloroe hane ND 6.4 Tetrachloroethene ND 6.4 1,3-Dichloropro~ane ND 6.4 1,1,1,2-Tetrach oroethane ND 6".4 Dibromochloromethane ND 6.4 Ethylene Dibromide ND 6.4 Chlorobenzene ND 6.4 Bromoform ND 6.4 lhl,2,2-Tetrachloroethane ND 6.4 C lorotoluene ND 6.4 1,3-Dichlorobenzene ND 6.4 1,4-Dichlorobenzene ND 6.4 1,2-Dichlorobenzene ND 6.4 Benzylchloride ND 6.4 SURROGATE PARAMETER % RECOVERY QC LIMIT --------- --------- Bromofluorobenzene 110 60-140 MDL: Method Detection Limit CKY INC., ANALYTICAL lABORATORIES, 630 Maple Ave .. Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I I 1- EPA METHOD 8010 HALOGENATED VOLATILE ORGANICS CLIENT: PROJECT: Ogden Environmental DATE COLLECTED~--02/11/96 Cfiula Vista DATE RECEIVED: 02/12/96 BATCH NO.: 96B042 DATE EXTRACTED: NA BWB504S03D86.0 DATE ANALYZED: 02/13/96SAMPLEID: CONTROL NO. : MOISTURE: B042-06 MATRIX: SOIL 26.6 DILUTION FACTOR: 1 RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Dichlorodifluoromethane ND 34.1 Chloromethane ND 34.1 Vinyl Chloride ND 34.1 Bromomethane ND 34.1 Chloroethane ND 34.1 Trichlorofluoromethane ND 6.81 1,1-Dichloroethene ND 6.81 Meth1lene Chloride ND 34.1 cis-,2-Dichloroethene ND 6.81 trans-lh2-Dichloroethene ND 6.81 lhl-Dic loroethane 15 6.81 C loroform ND 6.81 1,101-Trichloroethane ND 6.81 Car on Tetrachloride ND 6.81 1,2-Dichloroethane ND 6.81 Trichloroethene. 240 6.81 1,2-Dichloropropane ND 6.81 Dibromomethane ND 6.81 Bromodichloromethane ND 6.81 2-Chloroethyl vinylether ND 6.81 trans-1,3-Dichloropropene ND 6.81 cis-1,3-DichloroEropene ND 6.81 1,1,2-Trichloroe hane 12 6.81 Tetrachloroethene 11 6.81 1,3-Dichloropro~ane ND 6.81 1,1,1,2-Tetrach oroethane ND 6.81 Dibromochloromethane ND 6.81 Ethylene Dibromide ND 6.81 Chlorobenzene ND 6.81 Bromoform ND 6.81 lhl,2,2-Tetrachloroethane ND 6.81 C lorotoluene ND 6.81 1,3-Dichlorobenzene ND 6.81 1,4-Dichlorobenzene 12 6.81 1,2-Dichlorobenzene 9.0 -6.81 Benzylchloride ND 6.81 SURROGATE PARAMETER % RECOVERY QC LIMIT ------------------------------ - - - - Bromofluorobenzene 119 60-140 MDL: Method Detection Limit I ~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave., Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I EPA METHOD 8010 HALOGENATED VOLATILE ORGANICS CLIENT: Ogden Environmental DATE COLLECTED: NA PROJECT: Cfiula Vista DATE RECEIVED: NA BATCH NO.: 96B042 DATE EXTRACTED: NA SAMPLE ID: MBLKlS DATE ANALYZED: 02/12/96 CONTROL NO.: VAL587B MATRIX: SOIL MOISTURE: NA DILUTION FACTOR: 1 =============================-========--======-===================== RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Dichlorodifluoromethane ND 25 Chloromethane ND 25 Vinyl ·chloride ND 25 Bromomethane ND · 25 Chloroethane ND 25 Trichlorofluoromethane ND 5 1,1-Dichloroeth~ne ND 5 Meth1lene Chloride ND 25 cis-,2-Dichloroethene ND 5 trans-ln2-Dichloroethene ND 5 lnl-Dic loroethane ND 5 C loroform ND 5 1,161-Trichloroethane ND 5 Car on Tetrachloride ND 5 1,2-Dichloroethane ND 5 Trichloroethene ND 5 1,2-Dichloropropane ND 5 D1bromomethane ND 5 Bromodichloromethane ND 5 2-Chloroethyl vinylether ND 5 trans-1,3-Dichloropropene ND 5 cis-1,3-Dichlorofropene ND 5 1,1,2-Trichloroe hane ND 5 Tetra~hloroethene ND 5 1,3-Dichloropro~ane ND 5 1,1,l,2-Tetrach oroethane ND 5 D1bromochloromethane ND 5 Ethylene Dibromide ND 5 Chlorobenzene ND 5 Bromoform ND 5 lnl,2,2-Tetrachloroethane ND 5 C lorotoluene ND 5 1,3-Dichlorobenzene ND 5 1,4-Dichlorobenzene ND 5 1,2-Dichlorobenzene ND 5 Benzylchloride ND 5 SURROGATE PARAMETER % RECOVERY QC LIMIT --- - - - - - - -------------------- ---- Bromofluorobenzene 115 60-140 MDL: Method Detection Limit 1~-~--- I ~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618·8889 Fax: (310) 618-0818 I I IENT: Ogden Environmental OJECT: Chula Vista THOD: EPA 8010 MATRIX: SOIL CKY QUALITY CONTROL DATA MS/MSD ANALYSIS MOISTURE: 8.9 . -== == BATCH NO. : 96B042 DA TE RECEIVED: 02/ 12/96 SAMPLE ID: BWB505S01D10.0 DATE EXTRACTED: NA I NTROL NO.: B042-01 . DATE ANALYZED: 02/12/96 CESSION: 96B042 RAMETER SMPL RSLT SPIKE AMT MS RSLT MS SPIKE AMT MSD RSLT MSD RPD QC LIMIT RPD LIMIT ug/kg) (ug/kg) Cug/kg) % REC Cug/kg) (ug/kg) % REC % % % 1-Dichloroethene ND 274.00 284.00 103 274.00 277.00 101 3 60-140 40 Trichloroethene ND 274.00 282.00 103 274.00 280.00 102 0 60-140 40 lorobenzene ND 274.00 302.00 110 274. 00 302.00 110 0 60-140 40 IRROGATE PARAMETER Bromofluorobenzene I I I I I I I I I I SPIKE AMT MS RSLT MS SPIKE AMT MSD RSLT MSD QC LIMIT ug/kg) (ug/kg) % REC (ug/kg) (ug/kg) % REC % 274.00 279.00 102 274.00 292.00 106 60·140 1 -··-------,~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: !310) 618-0818 I I IENT: Ogden Environmental OJECT: Chula Vista THOD: EPA 8010 MATRIX: SOIL MOISTURE: NA CKY QUALITY CONTROL DATA LCS/LCD ANALYSIS BATCH NO.: 968042 DATE RECEIVED: NA SAMPLE ID: LCS1S/LCS1SD DATE EXTRACTED: NA INTROL NO.: VAL587L/C DATE ANALYZED: 02/12/96 CESSION: 968042 R.AMETER BLNK RSLT SPIKE AMT BS RSLT BS SPIKE AMT BSD RSLT BSD RPO QC LIMIT RPO LIMIT ug/kg) (ug/kg) (ug/kg) % REC (ug/kg) (ug/kg) % REC % % % 1-Dichloroethene ND 100.00 123.00 123 100.00 122.00 122 1 70-125 40 Trichloroethene ND 100.00 119.00 119 100.00 124.00 124 4 70-125 40 llorobenzene ND 100.00 121.00 121 100.00 119.00 119 2 70-125 40 RROGATE_PARAMETER Bromofluorobenzene I I I I I I I I I SPIKE AMT BS RSLT BS SPIKE AMT BSD RSLT BSD QC LIMIT ug/kg) (ug/kg) % REC (ug/kg) (ug/kg) % REC % 250.00 259.00 104 250.00 240.00 96 60·140 I 1~---, ~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (31 OJ 618-0818 I I I I I I I I I I I I I I I I I CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO . : MOISTURE: EPA METHOD 8020 BTEX Oqden Environmental DATE COLLECTED~ 02/10/96 Cfiula Vista DATE RECEIVED: 02/12/96 96B042 DATE EXTRACTED: NA BWB505S01D10.0 DATE ANALYZED: 02/12/96 B042-01 MATRIX: SOIL 8.9 DILUTION FACTOR: 1 =---------------------------------------=-------========--===-----== RESULTS PARAMETERS (ug/kg) MDL ug/kg) ------------------------ Benzene ND 5.49 Toluene ND 5.49 Ethylbenzene ND 5.49 Total Xylenes ND 16.5 SURROGATE PARAMETER % RECOVERY QC LIMIT ----------------------------- - - - Bromofluorobenzene 65 60-140 MDL: Method Detection Limit 1-~-----~---~--- I ~ CKY INC., ANALYTICAL lABORATORIES, 630 Maple Ave .. Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO . : MOISTURE: EPA METHOD 8020 . BTEX Ogden Environmental DATE COLLECTED: 02/.10/.96 Cfiula Vista DATE RECEIVED: 02/12/96 96B042 DATE EXTRACTED: NA BWB505S04D85.5 DATE ANALYZED: 02/12/96 B042-02 MATRIX: SOIL 23.1 DILUTION FACTOR: 1 RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Benzene ND 6.5 Toluene ND 6.5 Ethylbenzene ND 6.5 Total Xylenes ND 19.5 SURROGATE PARAMETER ~ 0 RECOVERY QC LIMIT ----------------------------- - - - Bromofluorobenzene 65 60-140 MDL: Method Detection Limit I 1---- I ~ CKY INC., ANALYTICAL lABORATORIES, 630 Maple Ave .. Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I 1. CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO . : MOISTURE: EPA METHOD 8020 BTEX Ogden Environmental DATE COLLECTED~--02/10/96 Cnula Vista DATE RECEIVED: 02/12/96 96B042 DATE EXTRACTED: NA BWB505S05D91 DATE ANALYZED: 02/12/96 B042-03 MATRIX: SOIL 20.1 DILUTION FACTOR: 1 ============================================================· ======= RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Benzene ND 6.26 Toluene ND 6.26 Ethylbenzene ND 6.26 Total Xylenes ND 18.8 SURROGATE PARAMETER % RECOVERY QC LIMIT ---------------------------- - - - - Bromofluorobenzene 40+ 60-140 MDL: MethQd Detection Limit Outside QC limits, sample was reanalyzed on 02/14/96. I G<t CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (3101618-0818 I I I I I I I I I I I I I I I I I EPA METHOD 8020 BTEX CLIENT: Oqden Environmental DATE COLLECTED: 02/10/96 PROJECT: Cfiula Vista DATE RECEIVED: 02/12/96 BATCH NO.: 96B042 DATE EXTRACTED: NA SAMPLE ID: BWBSOSSOSD91 DATE ANALYZED: 02/14/96 CONTROL NO.: B042-03R MATRIX: SOIL MOISTURE: 20.1 DILUTION FACTOR: 1 =====================-=======-=========-============================ PARAMETERS RESULTS ug/kg) MDL ug/kg) ------------------------ Benzene ND 6.26 Toluene ND 6.26 Ethylbenzene ND 6.26 Total Xylenes ND 18.8 SURROGATE PARAMETER % RECOVERY QC LIMIT --------- --------- Bromofluorobenzene 50+ 60-140 MDL: Method Detection Limit + Outside QC limits on the reanalysis run 1---- I ~ CKY INC., ANALYTICAL lABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618·8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO. : MOISTURE: EPA METHOD 8020 BTEX Ogden Environmental DATE COLLECTED~ -02/11/96 Cfiula Vista DATE RECEIVED: 02/12/96 96B042 DATE EXTRACTED: NA BWB504S01D26.5 DATE ANALYZED: 02/12/96 B042-04 MATRIX: SOIL 6.6 DILUTION FACTOR: 1 RESULTS 'DLPARAMETERS (ug/kg) (ug kg) ------------------------ Benzene ND 5.35 Toluene ND 5.35 Ethylbenzene ND 5.35 Total Xylenes ND 16.1 SURROGATE PARAMETER % RECOVERY QC LIMIT ---------------------------- - - - - Bromofluorobenzene 66 60-140 MDL: Method Detection Limit I 1-~-- I ~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave., Torrance. Calif. 90503 Tel. (31~) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I I EPA METHOD 8020 BTEX CLIENT: Ogden Environmental DATE COLLECTED: 02/.11/.96 PROJECT: Cfiula Vista DATE RECEIVED: 02/12/96 BATCH NO.: 96B042 DATE EXTRACTED: NA SAMPLE ID: BWB504S02D76.5 DATE ANALYZED: 02/13/96 CONTROL NO.: B042-05 MATRIX: SOIL MOISTURE: 21.9 DILUTION FACTOR: 1 =============================--=======---=====---=================== RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Benzene ND 6.4 Toluene ND 6.4 Ethylbenzene ND 6.4 Total Xylenes ND 19.2 SURROGATE PARAMETER % RECOVERY QC LIMIT ---------------------------- - - - - Bromofluorobenzene 65 60-140 MDL: Method Detection Limit 1-- I ~ CKY INC., ANALYTICAL lABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I I EPA METHOD 8020 BTEX CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO. : MOISTURE: Ogden Environmental Cfiula Vista 96B042 BWB504S03D86.0 B042-06 26.6 DATE COLLECTED: 02/11/96 DATE RECEIVED: 02/12/96 DATE EXTRACTED: NA DATE ANALYZED: 02/13/96 MATRIX: SOIL DILUTION FACTOR: 1 ========================================--====--==================== RESULTS MDL PARAMETERS (ug/kg) (ug/kg) ------------------------ Benzene ND 6.81 Toluene ND 6.81 Ethylbenzene ND 6.81 Total Xylenes ND 20.4 SURROGATE PARAMETER % RECOVERY QC LIMIT ------------------------------- - Bromofluorobenzene 66 60-140 MDL: Method Detection Limit I~----------- I G\, CKY INC., ANALYTICAL IABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I I 1-- CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO . : MOISTURE: EPA METHOD 8020 BTEX O~den Environmental DATE COLLECTED~--NA-===== Cfiula Vista DATE RECEIVED: NA 96B042 DATE EXTRACTED: NA MBLKlS DATE ANALYZED: 02/12/96 VAL587B MATRIX:. SOIL NA DILUTION FACTOR: 1 PARAMETERS RESULTS ug/kg) MDL ug/kg) ------------------------ Benzene ND 5 Toluene ND 5 Ethylbenzene ND 5 Total Xylenes ND 15 SURROGATE PARAMETER % RECOVERY QC LIMIT ------------------------------ - - Bromofluorobenzene 71 60-140 MDL: Method Detection Limit I ~ CKY INC., ANALYTICAL lABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I I 1- EPA METHOD 8020 BTEX CLIENT: Ogden Environmental DATE COLLECTED: NA PROJECT: Cfiula Vista DATE RECEIVED: NA BATCH NO.: 96B042 DATE EXTRACTED: NA SAMPLE ID: MBLK2S DATE ANALYZED: 02/14/96 CONTROL NO.: VAL597B MATRIX: SOIL MOISTURE: NA DILUTION FACTOR: 1 PARAMETERS Benzene Toluene Ethylbenzene Total Xylenes SURROGATE PARAMETER Bromofluorobenzene MDL: Method Detection Limit RESULTS ug/kg) ND ND ND ND RECOVERY --------- 65 MDL ug/kg) 5 5 5 15 QC LIMIT - - - - - 60-140 I ~ CKY INC., ANALYTICAL lABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I IENT: Ogden Environmental OJECT: Chula Vista THOO: EPA 8020 MATRIX: SOIL CKY QUALITY CONTROL DATA MS/MSD ANALYSIS MOISTURE: 8.9 BATCH NO.: 968042 DATE RECEIVED: 02/12/96 SAMPLE ID: B\.IB505S01D10.0 DATE EXTRACTED: NA I NTROL NO.: 8042-01 DATE ANALYZED: 02/13/96 CESSION: 968042 SMPL RSLT SPIKE AMT MS RSLT MS SPIKE AMT MSD RSLT MSD RPD QC LIMIT RPD LIMIT ,~~~:::~ ( ug/kg) (ug/kg) (ug/kg) % REC (ug/kg) (ug/kg) % REC % % % ---·----------------------------------------------------------- --------------------------- nzene ND 274.00 228.00 83 274.00 226.00 82 1 60-140 40 Toluene ND 274.00 223.00 81 274.00 223.00 81 0 60-140 40 lhylbenzene ND 274.00 237.00 86 274.00 237.00 86 0 60-140 40 tal Xylenes ND 823.00 597.00 73 823.00 598.00 73 0 60-140 40 RROGATE PARAMETER omofluorobenzene I I I I I I I I I _, ___ ------ SPIKE AMT ug/kg) 274.00 MS RSLT MS ug/kg) % REC 284.00 104 SPIKE AMT MSD RSLT MSD QC LIMIT ug/kg) (ug/kg) % REC % 274.00 278.00 101 60-140 CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: {3 lOl 6 l s-0818 I I IENT: Ogden Envirorvnental OJECT: Chula Vista THOD: EPA 8020 MATRIX: SOILIMOISTURE: NA . CKY QUALITY CONTROL DATA LCS/LCD ANALYSIS BATCH NO.: 968042 DATE RECEIVED: NA SAMPLE ID: LCS1S/LCS1 SD DATE EXTRACTED: NA IONTROL NO.: VAL587L/C DATE ANALYZED: 02/12/96 CCESSION: 968042 nzene Toluene lhylbenzene tal Xylenes RROGATE PARAMETER BLNK RSLT ug/kg) ND ND ND ND SPIKE AMT ug/kg) SPIKE AMT BS RSLT ug/kg) (ug/kg) 100.00 88.50 100.00 90.00 100.00 100.50 300.00 248.00 BS RSLT ug/kg) BS REC BS REC 88 90 101 83 SPIKE AMT BSD RSLT BSD ug/kg) (ug/kg) % REC 100.00 100.00 100.00 300.00 SPIKE AMT ug/kg) 88.00 89.00 104.00 261.00 BSD RSLT Ug/kg) 88 89 104 87 RPO BSD REC 1 1 2 5 QC LIMIT RPO LIMIT 70-125 40 70-125 40 70-125 40 70-125 40 QC LIMIT omofluorobenzene 250.00 252.00 101 250.00 249.00 100 60-140 I I I I I I I I I CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I IIENT: Ogden Environmental OJECT: Chula Vista THOD: EPA 8020 MATRIX: SOIL CKY QUALITY CONTROL DATA LCS/LCD ANALYSIS MOISTURE: NA . BATCH NO.: 968042 DATE RECEIVED: NA MPLE ID: LCS2S/LCS2SD DATE EXTRACTED: NA NTROL NO.: VAL597L/C DATE ANALYZED: 02/14/96 CESSION: 968042 BLNK RSLT SPIKE AMT BS RSLT BS SPIKE AMT BSD RSLT BSD RPO QC LIMIT RPO LIMIT ug/kg) (ug/kg) (ug/kg) % REC (ug/kg) (ug/kg) % REC % % % Benzene ND 100.00 90.00 90 100.00 87.00 87 3 70·125 40 Toluene ND 100.00 91.50 92 100.00 88.50 88 3 70·125 40 lhylbenzene ND 100.00 88.50 89 100.00 96.50 97 9 70·125 40 tal Xylenes ND 300.00 240.00 80 300.00 232.00 77 4 70-125 40 SPIKE AMT BS RSLT BS SPIKE AMT BSD RSLT BSD QC LIMIT RROGATE PARAMETER (ug/kg) (ug/kg) % REC (ug/kg) (ug/kg) % REC % omofluorobenzene I I I I I I I I I 1--------~-- 250.00 246.00 99 250.00 244.00 98 60-140 CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I I STERLING Analytical Laboratory CKY Inc. Analytical Laboratories 630 Maple Aven~, Torrance, CA 90503 Attn: Dr. W. Nisamaneepong Job No.: 0691081.00 Project Name: Ogden Folder No.: 4270 LABORATORY REPORT February 21, 1996 Page.1 of 1 Samples: Six (6) soil samples from 96B042-0dgen, collected on 02/10/96 and 02/11/96 and received on 02/12/96. Sample ID 96B042-1 96B042,-2 96B042-3 96B042-4 96B042-S 96B042-6 Reporting Limit Date Analyzed TOC Walkley Black) 0.027 0.011 0.072 0.079 0.019 0.015 0.010 02/20/96 Reviewed by 1--------C4--270 . -rep---- Approved by 2860 Walnut Avenue I Long Beach, CA 90806-1 834 1800) 366-9324 • 1310) 595-9324 1310) 595-6709 FAX I I I I I I I I I I I I I I I I I I I STERLING Analytical Laboratory Quality Assurance Addendum Report Page 1 of 1 QA/QC Results LAB ID SYMBOL--TEST UNITS Sample Dup. · RPD (%) 4270-6 TOC % 0.015 0.011 28 Notes: Note that Matrix Spikes are not project specific. Therefore, spike information shown on this report may not be from the same project; however, they were analyzed in the same analytical batch. Definitions: Spike: A sample from the analytical batch which has been spiked with the parameter(s) of interest at a known concentration and taken through the same preparation and analysis as the samples. Spike Duplicate: A duplicate of the spiked sample, taken from a separate aliquot of the sample. RPD: Mean: Relative Percent Difference between a Spike and a Spike Duplicate (or a sample and sample duplicate). RPD = [(Spike-Spk. Dup.)/Mean] * 100 Where the mean is the average spike recovery of the matrix spike and the matrix spike duplicate. The average sample results, from both samples and sample duplicates. Control limits are calculated by Sterling Analytical Laboratory for internal use from existing spike data. Control limits are found by calculating three standard deviations above and below the mean of the population. C4270.qa I I-- - - --- - --- -I I CHAIN Of' CUSTODY RECORD CLl~NT NAME: ck.Y I>JC. ~-nCAL Ut6, REQUEST FOR ANALYSIS I ADDRESS: l#3o MAPL.E AVE. DATE: 10fYVttJc1:. , CA 9.oSDa PAGE OF PH~NE NoJ5lo)l,/8-&&Sq FAX NO. (310)(,/0-00/8 ----- PROJECT NAME: t.' t!it:J42. -Of; PS/J SEND REPORT TO: "B:, w. fllS'i-MA-Nl:EfON<:; I TURN AROUND 7 SAMPLER NAME/SIGNATURE NORMAL · . ! i RUSH (\j .- 1a D i ILO I I SAMPLE SAMPLING PRESER-CONTAINER SAMPLE DESCRIPTION cxi :il ~ : il ~ i NUMBER DATE/TIME VATIVE SIZE/TYPE WATER SOIL OTHER v :i: I I lo I "1'1qt,&of-2-I D43o )c i I . JI ;oIz )( J I ',od , 1, J,l.,U, X I i 1-hl '1.11, D'l4& )( c:; I J. I il4'2-I X 4 j, (, i }"1,7& )( I I I I I I I i I I I I I I COM~ENTS: I i Re~ished by: (Si nature) :i.°:}) ,'fl J:;;_~ Relinquished by: (Signature) Date: Comp~ny Time: Company: t:J (J Time: Company: Time: I CK Y incorporated Analytical Laboratories 630 Maple Ave. Torrance, Calif. 90503 Tel: 310-618·8889 Fax: 310-618-0818 i ANALYSES REQUIRED IiIf) 7ii ; v LO Q) Ill C'C· (\j N CD ~ :i: ! l'q 0v ..... ~ \,)~QNN O <O 0 ~Id IS" X I( X X Received by: (Signature) Date: Company: Time: I_Cl~ _________ IJ <tr .!f:£?<t.1AJ £. t.A:S /:1?.r .• . . tu, ade/[Jq.,csal of Sam pies. Sa,nple will be storecJ at CKY for 30 days at r,o charge arid at$ t0/sa111ple/month thereafter. Disposal of sample by the Laboratory will be charged at $10/sample. 1-- - -AnalyticalTechnologies,lrlc.. I PROJECT MANAGER: I COMPANY: I ADDRESS: I Comments: I i I 5550 MOREHOUSE DRIVE SAN DIEGO. CA 92121-1109 619) 458-9141 0 Return t Chai~ of Custody 'f'1/364Jt.. DATE "2.JJJ I 'Jt, PAGE-L OF _l_ l.JJ_ V I f( Recommended Quantity and Prese111allve (Provide triple volume on QC Samples) 1 · · I·-~·' X. I ; Signature: Printed Name: · Date: Printed Name: Date: Printed Name: Date: Company: Company: Analytical Technologies, Inc. OlsrRJBUTION: While, CBne,y . ANALYTICAL TECHNOWGIES, INC • Pink . ORIGINATOR i'.itt' A SAMPLE RECEIPT FORM CONTROL NO. 96804-2 DATE 02-i'1.. -96 CLIENT O&f)EN TIME 11:lo~ PROJECT C#IJI..A ViSTA RECIPIENT C, 'Tl4-"1GCO SAMPLE TRANSPORTATION TO CKY LABORATORY: BY ON(DATE) ATCTIMEl FROM(SITE/CO.) COMMENTS PICKED-UP BY CKY COURIER ' D~LIVERED BY CLIENT./ SHIPPED/AIRBILL NOW,,,·· PM bet.> ,3c.J73:2.,8 -s1:e R.Ect;iP1 SAMPLE BATCH PACKAGING/SEALING UPON RECEIPT: NO CONTAINER ./iNTACT DAMAGED NOT SEALED /SEALED CONT~INER: INSIDE TEMPERATURE: 4,c. C CUSTODY SEAL /OTHER SEAL LOCATION NUMBER VcoOLER PACKAGING TYPE SUFFICIENCY /INTACT DAMAGED I BOX INSULATION: OK NAME: .A-,:.OIJNJ> CUJWKJ=. ) OTHER: ICE/COOLANT: ,JUJ)& iC.I:. I DATE: _!_ i PACKING MATERIAL: i./C>tJls. t TIME: SAMPLE DOCUMENTATION/CHAIN-OF-CUSTODY(COC) NONE . ./HANDCARRIED ENCLOSED FAXED SEALED. SAMPLE LOG-IN: CRITERIA COMMENTS DISCREPANCY ./ SAMPLE CUSTODY SEAL EVERY SAMPLE ND"1e ~ CdNTAI NER TYPE/MATERIAL APPROPRIATE o/c: ~ SAMPLE AMOUNT ENOUGH ~ SAMPLE PRESERVATION/HOLDING TIME SUFFICIENT / HEADSPACE/BUBBLES ZERO/NONE r / SAMPLE LABEL INFORMATION SUFFICIENT 11 P.~-,,,_ .~. I ./ CHAIN-OF-CUSTODY INFORMATION SUFFICIENT IJ V --.. -' SAMPLE INFO.: SAMPLE ID / DATE / TIME ./'J SIGNATURE /] ANALYSES / PRESERVATIVE CONTAINER / INDIVIDUAL SAMPLE CONTAINER: NONE PLASTIC BAG CAN OTHER(SPECIFY): SEALED sAMPL.E NUMBER CLIENT ID DISCREPANCY ACTION I bRJ<:;IIJAL eoc WA~ tJOT AEc 1D DIJJ.A!J / I / DU!'UCATE w'A~ RF£1D _.,,,,,. I I / _.,,,,,.. ~ I / ~ / I I / ~ / I JV ~ 7 i / _.,,,,,. / I / ~ / 7 ,/' ' / c,tf/ ......-: DATE -TIME I I I I I I I I I I I I I I I EPA METHOD 8010 HALOGENATED VOLATILE ORGANICS CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO. : MOISTURE: Ogden Environmental Brandywine 96Bl34 MWOl-SOl Bl34-01 NA DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: 02/27/96 02/28/96 NA 03/10/96 WATER 1 RESULTS MDL PARAMETERS (ug/L) (ug/L) ---------------------- Dichlorodifluoromethane ND 5 Chloromethane ND 5 Vinyl Chloride ND 5 Bromomethane ND 5 Chloroethane ND 5 Trichlorofluoromethane ND 1 1,1-Dichloroethene ND 1 Meth1lene Chloride 87 5 cis-,2-Dichloroethene ND 1 trans-1,2-Dichloroethene ND 1 1,1-Dichloroethane ND 1 Chloroform ND 1 1,1,1-Trichloroethane ND 1 Carbon Tetrachloride ND 1 1,2-Dichloroethane ND 1 Trichloroethene 13 1 1<2-Dichloropropane ND 1 Dibromomethane ND 1 Bromodichloromethane ND 1 2-Chloroethyl vinylether ND 1 trans-1,3-Dichloropropene ND 1 cis-1,3-Dichlorofropene ND 1 1,1,2-Trichloroe hane ND 1 Tetrachloroethene ND 1 1,3-Dichloropro~ane ND 1 1<1,1,2-Tetrach oroethane ND 1 Dibromochloromethane ND 1 Ethylene Dibromide ND 1 Chlorobenzene ND 1 Bromoform ND 1 1,1,2,2-Tetrachloroethane ND 1 Chlorotoluene ND 1 1,3-Dichlorobenzene ND 1 1,4-Dichlorobenzene ND 1 1,2-Dichlorobenzene ND 1 Benzylchloride ND 1 SURROGATE PARAMETER % RECOVERY QC LIMIT Bromofluorobenzene 68 65-135 I · MDL: Method Detection Limit I I I I <+v CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618·8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I I I EPA METHOD 8010 HALOGENATED VOLATILE ORGANICS CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO. : MOISTURE: Ogden Environmental Brandywine 96B13~ MW02-S01 B134-02 NA DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: 02/27/96 02/28/96 NA 03/10/96 WATER 1 RESULTS MDL PARAMETERS (ug/L) (ug/L) ---------------------- Dichlorodifluoromethane ND 5 Chloromethane ND 5 Vinyl Chloride ND 5 Bromomethane ND 5 Chloroethane ND 5 Trichlorofluoromethane ND 1 1,1-Dichloroethene 19 1 Meth1lene Chloride 55 5 cis-,2-Dichloroethene ND 1 trans-1,2-Dichloroethene ND 1 1,1-Dichloroethane ND 1 Chloroform ND 1 1,1,1-Trichloroethane ND 1 Carbon Tetrachloride ND 1 1,2-Dichloroethane ND 1 Trichloroethene 1. 6 1 1 1 2-Dichloropropane ND 1 Dibromomethane ND 1 Bromodichloromethane ND 1 2-Chloroethyl vinylether ND 1 trans-1,3-Dichloropropene ND 1 cis-1~3-Dichloropropene ND 1 1,1,2-Trichloroethane ND 1 Tetrachloroethene ND 1 1,3-Dichloropro~ane ND 1 1,1,1,2-Tetrach oroethane ND 1 Dibromochloromethane ND 1 Ethylene Dibromide ND 1 Chlorobenzene ND 1 Bromoform ND 1 1,1,2,2-Tetrachloroethane ND 1 Chlorotoluene ND 1 1,3-Dichlorobenzene ND 1 1,4-Dichlorobenzene ND 1 1,2-Dichlorobenzene ND 1 Benzylchloride ND 1 SURROGATE PARAMETER % RECOVERY QC LIMIT ------------------------------ - - Bromofluorobenzene 66 65-135 MDL: Method Detection Limit I ~ CKY INC .. ANALYTICAL IABORATORIES. 630 Maple Ave .. Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I EPA METHOD 8010 HALOGENATED VOLATILE ORGANICS CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO. : MOISTURE: Ogden Environmental Brandywine 96B13-l MW03-S01 B134-03 NA DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: 02/27/96 02/28/96 NA 03/11/96 WATER 1 RESULTS MDL PARAMETERS (ug/L) (ug/L) ---------------------- Dichlorodifluoromethane ND 5 Chloromethane ND 5 Vinyl-Chloride ND 5 Bromomethane ND 5 Chloroethane ND 5 Trichlorofluoromethane ND 1 1,1-Dichloroethene 22 1 Meth1lene Chloride 68 5 cis-,2-Dichloroethene 11 1 trans-1,2-Dichloroethene ND 1 1,1-Dichloroethane 60 1 Chloroform 16 1 1,1,1-Trichloroethane ND 1 Carbon Tetrachloride ND 1 1,2-Dichloroethane 4.3 1 Trichloroethene 400 1 1 1 2-Dichloropropane ND 1 Dibromomethane ND 1 Bromodichloromethane ND 1 2-Chloroethyl vinylether ND 1 trans-1,3-Dichloropropene ND 1 cis-1,3-Dichloro~ropene ND 1 1,1,2-Trichloroe hane 31 1 Tetrachloroethene 26 1 1,3-Dichloropro~ane ND 1 1(1,1,2-Tetrach oroethane ND 1 Dibromochloromethane ND 1 Ethylene Dibromide ND 1 Chlorobenzene ND 1 Bromoform ND 1 1,1,2,2~Tetrachloroethane ND 1 Chlorotoluene ND 1 1,3-Dichlorobenzene ND 1 1,4-Dichlorobenzene ND 1 1,2-Dichlorobenzene ND 1 Benzylchloride ND 1 SURROGATE PARAMETER 9- 0 RECOVERY QC LIMIT ----------------------------- - - - Bromofluorobenzene 76 65-135 I MDL: Method Detection Limit I I I CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310\ 618-0818 I I I I I I I I I I I I I I EPA METHOD 8010 HALOGENATED VOLATILE ORGANICS CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO. : MOISTURE: PARAMETERS ---------- Ogden Environmental Brandywine 96B134 MW05-S01 B134-04 NA Dichlorodifluoromethane Chloromethane Vinyl Chloride Bromomethane Chloroe thane Trichlorofluoromethane 1,1-Dichloroethene Meth1lene Chloride cis-,2-Dichloroethene trans-1,2-Dichloroethene 1,1-Dichloroethane Chloroform 1,1,1-Trichloroethane Carbon Tetrachloride 1,2-Dichloroethane Trichloroethene 1<2-Dichloropropane D1bromomethane Bromodichloromethane 2-Chloroethyl vinylether trans-1,3-Dichloropropene cis-1,3-Dichloropropene 1,1,2-Trichloroethane Tetrachloroethene 1,3-Dichloropro~ane 1<1,1,2-Tetrach oroethane D1bromochloromethane Ethylene Dibromide Chlorobenzene Bromoform 1,1,2,2-Tetrachloroethane Chlorotoluene 1,3-Dichlorobenzene 1,4-Dichlorobenzene 1,2-Dichlorobenzene Benzylchloride SURROGATE PARAMETER ------------------ Bromofluorobenzene DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: RESULTS 02/27/96 02/28/96 NA 03/11/96 WATER 1 MDL ug/L) (ug/L) ------------ ND 5 ND 5 ND 5 ND 5 ND 5 ND 1 ND 1 30 5 ND 1 ND 1 ND 1 ND 1 ND 1 ND 1 ND 1 3.0 1 ND 1 ND 1 ND 1 ND 1 ND 1 ND 1 ND 1 ND 1 ND 1 ND 1 ND 1 ND 1 ND 1 ND 1 ND 1 ND 1 ND 1 ND 1 ND 1 ND 1 RECOVERY QC LIMIT --------- - - - - 67 65-135 I ·MDL: Method Detection Limit I I I I --~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave., Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (3101 6 l :,-1l'ii8 I I I I I I I I I I I I I I I I I I EPA METHOD 8010 HALOGENATED VOLATILE ORGANICS CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO . : MOISTURE: Ogden Environmental Brandywine 96B134 MW04-S01 B134-05 NA DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: 02/27/96 02/28/96 NA 03/11/96 WATER 1 RESULTS MDL PARAMETERS (ug/L) (ug/L) ---------------- ------ Dichlorodifluoromethane ND 5 Chloromethane ND 5 Vinyl Chloride ND 5 Bromomethane ND 5 Chloroethane ND 5 Trichlorofluoromethane ND 1 1,1-Dichloroethene 67 1 Meth1lene Chloride 79 5 cis-,2-Dichloroethene 11 1 trans-1,2-Dichloroethene ND 1 1,1-Dichloroethane 76 1 Chloroform 16 1 1,1,1-Trichloroethane ND 1 Carbon Tetrachloride ND 1 1,2-Dichloroethane 24 1 Trichloroethene 720 1 1<2-Dichloropropane ND 1 D1bromomethane ND 1 Bromodichloromethane ND 1 2-Chloroethyl vinylether ND 1 trans-1,3-Dichloropropene ND 1 cis-1,3-~ichloropropene. ND 1 1,1,2-Tr1chloroethane 47 1 Tetrachloroethene 56 1 1,3-Dichloropro~ane ND 1 1<1,1,2-Tetrach oroethane ND 1 D1bromochloromethane ND 1 Ethylene Dibromide ND 1 Chlorobenzene ND 1 Bromoform ND 1 1,1,2,2-Tetrachloroethane ND 1 Chlorotoluene ND 1 1,3-Dichlorobenzene ND 1 1,4-Dichlorobenzene ND 1 1,2-Dichlorobenzene ND 1 Benzylchloride ND 1 SURROGATE PARAMETER % RECOVERY QC LIMIT ---------------------------- - - - - Bromofluorobenzene 80 65-135 MDL: Method Detection Limit I ~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (3 lOl 618-0818 I I I I I I I I I I I I I I EPA METHOD 8010 HALOGENATED VOLATILE ORGANICS CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO. : MOISTURE: Ogden Environmental Brandywine 96Bl34 MBLKlW VAL687B NA DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: NA NA NA 03/10/96 WATER 1 RESULTS MDL PARAMETERS (ug/L) (ug/L) ---------------------- Dichlorodifluoromethane ND 5 Chloromethane ND 5 Vinyl Chloride ND 5 Bromomethane ND 5 Chloroethane ND 5 Trichlorofluoromethane ND 1 1,1-Dichloroethene ND 1 Meth1lene Chloride ND 5 cis-,2-Dichloroethene ND 1 trans-1,2-Dichloroethene ND 1 1,1-Dichloroethane ND 1 Chloroform ND 1 1,1,1-Trichloroethane ND 1 Carbon Tetrachloride ND 1 1,2-Dichloroethane ND 1 Trichloroethene ND 1 1(2-Dichloropropane ND 1 D1bromomethane ND 1 Bromodichloromethane ND 1 2-Chloroethyl vinylether ND 1 trans-1,3-Dichloropropene ND 1 cis-1,3-Dichloro~ropene ND 1 1,1,2-Trichloroe hane ND 1 Tetrachloroethene ND 1 1,3-Dichloropro~ane ND 1 1,1,1,2-Tetrach oroethane ND 1 Dibromochloromethane ND 1 Ethylene Dibromide ND 1 Chlorobenzene ND 1 Bromoform ND 1 1,1,2,2-Tetrachloroethane ND 1 Chlorotoluene ND 1 1,3-Dichlorobenzene ND 1 1,4-Dichlorobenzene ND 1 1,2-Dichlorobenzene ND 1 Benzylchloride ND 1 SURROGATE PARAMETER % RECOVERY QC LIMIT Bromofluorobenzene 66 65-135 I MDL: Method Detection Limit I I I I CKY INC., ANALYTICAL lABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I IENT: Ogden Environmental OJECT: Brandywine. METHOD: EPA 8010 MATRIX: WATER CKY QUALITY CONTROL DATA LCS/LCD ANALYSIS I MO! STURE: NA BATCH NO.: AMPLE ID: ll°NTROL NO.: ACCESSION: 968134 LCS1W/LCS1WD VAL687LR/CR 968134 DATE RECEIVED: NA DATE EXTRACTED: NA DATE ANALYZED: 03/11/96 IARAMETER BLNK RSLT SPIKE AMT BS RSLT BS SPIKE AMT BSD RSLT BSD RPD QC LIMIT RPD LIMIT I•, 1-Dichloroethene richloroethene hlorobenzene ug/L) --------- ND ND ND ug/L) (ug/L) ------------------ 20.00 18.70 20.00 22.20 20.00 20.70 REC (ug/L) ---------------·-- 94 20.00 111 20.00 104 20.00 ug/L) % REC % % % 17. 70 88 5 70-125 30 20.40 102 8 70-125 30 21.10 106 2 70-125 30 I I I I I I I I I I I SPIKE AMT BS RSLT BS SPIKE AMT BSD RSLT BSD QC LIMIT ug/L) (ug/L) % REC (ug/L) (ug/L) % REC % 50.00 46.90 94 50.00 48.80 98 65-135 CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (3101 618-0818 I I I I I I I I I I I I I I I I I I EPA METHOD 8020 BTEX CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO . : MOISTURE: Ogden Environmental Brandywine 96B134 MWOl-SOl B134-01 NA DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: 02/27/96 02/28/96 NA 03/10/96 WATER 1 PARAMETERS RESULTS MDL ug/L) (ug/L) ---------------------- Benzene ND 1 Toluene ND 1 Ethylbenzene ND 1 Total Xylenes ND 3 SURROGATE PARAMETER % RECOVERY QC LIMIT ------------------------------- - Bromofluorobenzene 76 65-135 MDL: Method Detection Limit I ~ CKY INC., ANALYTICAL lABORATORIES, 630 Maple Ave .. Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I I EPA METHOD 8020 BTEX CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO . : MOISTURE: PARAMETERS ---------- Benzene Toluene Ethylbenzene Total Xylenes Ogden Environmental Brandywine 96Bl34 MW02-S01 B134-02 NA SURROGATE PARAMETER ------------------ Bromofluorobenzene MDL: Method Detection Limit DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: RESULTS 02/27/96 02/28/96 NA 03/10/96 WATER 1 MDL ug/L) (ug/L) ND 1 ND 1 ND 1 ND 3 RECOVERY QC LIMIT --------- ---- 65 65-135 I ,~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618·8889 Fax: (310\ ti 13-i',S 18 I I I I I I I I I I I I I I I I I I I EPA METHOD 8020 BTEX CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO . : MOISTURE: PARAMETERS ---------- Benzene Toluene Ethylbenzene Total Xylenes Ogden Environmental Brandywine 96B134 MW03-S01 B134-03 NA SURROGATE PARAMETER ------------------ Bromofluorobenzene MDL: Method Detection Limit DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: RESULTS 02/27/96 02/28/96 NA 03/11/96 WATER 1 MDL ug/L) (ug/L) ------------ ND 1 ND 1 ND 1 ND 3 RECOVERY QC LIMIT 100 65-135 CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I EPA METHOD 8020 . BTEX CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO. : MOISTURE: PARAMETERS ---------- Benzene Toluene Ethylbenzene Total Xylenes Ogden Environmental Brandywine 96Bl34 MW05-S01 Bl34-04 NA SURROGATE PARAMETER ------------------ Bromofluorobenzene DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: RESULTS 02/27/96 02/28/96 NA 03/11/96 WATER 1 MDL ug/L) (ug/L) ND 1 1. 9 1 ND 1 ND. 3 RECOVERY QC LIMIT 67 65-135 I -------------------------------------------------------------------- MDL: Method Detection Limit I I I I I I I I I I I I~ CKY INC.. ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I I I EPA METHOD 8020 BTEX CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO . : MOISTURE: PARAMETERS ---------- Benzene Toluene Ethylbenzene Total Xylenes Ogden Environmental Brandywine 96B13~ MW04-S01 B134-05 NA SURROGATE PARAMETER Bromofluorobenzene MDL: Method Detection Limit DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: RESULTS 02/27/96 02/28/96 NA 03/11/96 WATER 1 MDL ug/L) (ug/L) 7.1 1 ND 1 ND 1 ND 3 RECOVERY QC LIMIT 86 65-135 I Giy CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I I I EPA METHOD 8020 BTEX CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO. : MOISTURE: Ogden Environmental Brandywine 96B13'1 MBLKlW VAL687B NA DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: NA NA NA 03/10/96 WATER 1 RESULTS MDL PARAMETERS (ug/L) (ug/L) ---------------------- Benzene ND 1 Toluene ND 1 Ethylbenzene ND 1 Total Xylenes ND 3 SURROGATE PARAMETER % RECOVERY QC LIMIT ---------------------------- --- - Bromofluorobenzene 70 65-135 MDL: Method Detection Limit I ~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (:llO) 618-0818 I I IENT: Ogden Environmental OJECT: Brandywine METHOD: EPA 8020 MOISTURE: NA CKY QUALITY CONTROL DATA LCS/LCD ANALYSIS TRIX: WATER TCH NO.: 968134 DATE RECEIVED: NA MPLE ID: LCS1W/LCS1WD DATE EXTRACTED: NA NTROL NO.: VAL687LR/CR DATE ANALYZED: 03/11/96 ACCESSION: 968134 ARAMETER BLNK RSLT SPIKE AMT BS RSLT BS SPIKE AMT BSD RSLT BSD RPD QC LIMIT RPD LIMIT ug/L) (ug/L) (ug/L) % REC (ug/L) (ug/L) % REC % % % lnzene ND 20.00 17.60 88 20.00 17.60 88 0 70-125 30 luene ND 20.00 18.90 94 20.00 18.70 94 1 70-125 30 hylbenzene ND 20.00 20.50 102 20.00 20.50 102 0 70-125 30 Total Xylenes ND 60.00 54.10 90 60.00 54.20 90 0 70-125 30 IRROGATE PARAMETER Bromofluorobenzene I I I I I I I I I I SPIKE AMT BS RSLT BS SPIKE AMT BSD RSLT BSD QC LIMIT ug/L) (ug/L) % REC (ug/L) (ug/L) % REC % 50.00 50.60 101 50.00 51.50 103 65-135 I G\r CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: \3 lil) 6 i >-·Gt\ 18 I I I I I I I I I I I I I I I I I I I EPA METHOD 425.1 MBAS CLIENT: PROJECT: BATCH NO.: MATRIX: Ogden Environmental Brandywine 96Bl34 WATER DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: 02/27/96 02/28/96 NA 02/29/96 RESULT DILUTION MDL SAMPLE ID -coNTROL NO (mg/L) FACTOR (mg/L) ----------------------------------------- MWOl-SOl .· Bl34-01 0.1 1 .1 MW02-S01 Bl34-02 ND 1 .1 MW03-S01 Bl34-03 0.76 1 .1 MWOS-SOl Bl34-04 ND 1 .1 MW04-S01 Bl34-05 0.73 1 .1 MBLKlW MBBOOlWB ND 1 .1 MDL: Method Detection Limit CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: 1_3101 6 t S-il8 I 8 I CKY QUALITY CONTROL DATA DUPLICATE ANALYSIS IILIENT: Ogden E~vironmental 9ROJECT: Brandywine METHOD: EPA 425.1 MOISTURE: NAf TRIX: WATER BATCH NO.: 96B134 DATE RECEIVED: 02/28/96 PLE ID: MW02-SO~ DATE EXTRACTED: NA ONTROL NO.: B134-02 DATE ANALYZED: 02/29/96 ACCESSION: 96B134 IARAMETER SAMPLE mg/L) DUP. SAMPLE mg/L) RPD RPD LIMIT ND ND O 20 I I I I I I I I I I I I I CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance, Calif. 90503 Tel. (310) 618·8889 Fax: (310) 618-0818 I CKY QUALITY CONTROL DATA MS ANALYSIS LIENT: Ogden E~vironmental ROJECT: Brandywine ETHOD: EPA 425.1 MOISTURE: NAf TRIX: WATER BATCH NO.: 96B134 DATE RECEIVED: 02/28/96 IAMPLE ID: MWO 2 -SO 1 DATE EXTRACTED : NA ONTROL NO.: B134-02 DATE ANALYZED: 02/29/96 ACCESSION: 96B134 IARAMETER SMPL RSLT mg/L) SPIKE AMT mg/L) MS RSLT mg/L) MS QC LIMIT REC ( % ) . ND .50 .50 100 75-125 I I I I I I I I I I I I I CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I CKY QUALITY CONTROL DATA LCS ANALYSIS I IENT: Ogden Environmental OJECT: Brandywine THOD: EPA 425.1 MOISTURE: NAITRIX: WATER BATCH NO.: 96B134 DATE RECEIVED: NA PLE ID: LCSlW DATE EXTRACTED: NA 1fNTROL NO.: MBBOOlWL DATE ANALYZED: 02/29/96 ACCESSION: 96B134 LETER I I I I I I I I I I I BLNK RSLT mg/L) SPIKE AMT mg/L) LCS RSLT mg/L) LCS REC QC LIMIT ND .50 .52 104 85-115 I I~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (J 10, fi 18-0818 I I I I I I I I I I I I I I I I I I EPA METHOD 180.1 TURBIDITY CLIENT: PROJECT: BATCH NO.: MATRIX: Ogden Environmental Brandywine 96B134 WATER DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: 02/27/96 02/28/96 NA 02/29/96 ============---=---=-------==---=====------========================= RESULT DILUTION MDL SAMPLE ID -CONTROL NO (NTU) FACTOR (NTU) ----------------------------------------- MW01-S01 B134-01 303 20 20 MW02-S01 B134-02 258 20 20 MW03-S01 B134-03 3850 200 200 MW05-S01 B134-04 7240 200 200 MW04-S01 B134-05 684 40 40 MBLKlW TUB004WB ND 1 1 MDL: Method Detection Limit I G<t CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel..(310) 618·8889 Fax: (3101 1i 1.~-1 ,s 18 I CKY QUALITY CONTROL DATA DUPLICATE ANALYSIS a.,IENT: Ogden Ez:ivironmental OJECT: Brandywine METHOD: EPA 1B0.1 MOISTURE: NA [ TRIX: WATER BATCH NO.: 96B134 DATE RECEIVED: 02/28/96 PLE ID: MW02-S01 DATE EXTRACTED: NA 9]NTROL NO.: B134-02 DATE ANALYZED: 02/29/96 ACCESSION: 96B134 LETER 1.1rbidity I I I I I I I I I I I I SAMPLE NTU) DUP. SAMPLE NTU) RPD RPD LIMIT 258.00 269.00 4 20 I ~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (3Hl) 618-0818 I CKY QUALITY CONTROL DATA LCS ANALYSIS LIENT: Ogden Environmental ROJECT: Brandywine ETHOD: EPA 180.1 MATRIX: WATER 1-~~ISTURE: _ NA . ---------------------------------- BATCH NO. : 96B134 DATE RECEIVED: NA IAMPLE ID: LCSlW --DATE EXTRACTED: NA ONTROL NO.: TUB004WL DATE ANALYZED: 02/29/96 ACCESSION: 96B134 IARAMETER lurbidity I I I I I I I I I I I BLNK RSLT NTU) SPIKE AMT NTU) LCS RSLT NTU) LCS REC QC LIMIT ND 4.20 4.10 98 85-115 I I~ CKY INC.. ANALYTICAL lABORATORIES, 630 Maple Ave .. Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 6t8-0818 I I I I I I I I I I I I I I I I I I I EPA METHOD 310.1 TOTAL ALKALINITY CLIENT: PROJECT: BATCH NO.: MATRIX: Ogden Environmental Brandywine 96B13~ WATER DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: 02/27/96 02/28/96 NA 03/01/96 ===·================================================================ RESULT DILUTION MDL SAMPLE ID -CONTROL NO (mg/L) FACTOR (mg/L) ----------------------------------------- MW01-S01 B134-01 212 1 10 MW02-S01 B134-02 526 1 10 MW03-S01 B134-03 450 1 10 MW05-S01 B134-04 104 1 10 MW04-S01 B134-05 580 1 10 MBLKlW ALCOOlWB ND 1 10 MDL: Method Detection Limit CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618·8889 Fax: (310) 618-0818 I CKY QUALITY CONTROL DATA DUPLICATE ANALYSIS 11:..IENT: Ogden E~vironmental OJECT: Brandywine METHOD: EPA 310.1 MOISTURE: NAlTRIX: WATER BATCH NO.: 96B134 DATE RECEIVED: _02/28/96 PLE ID: MWOS-SOl -DATE EXTRACTED: NA NTROL NO.: B134-04 DATE ANALYZED: 03/01/96 ACCESSION: 96B134 lRAMETER rkalinity SAMPLE mg/L) DUP. SAMPLE mg/L) RPD RPD LIMIT 104.00 101.00 3 20 I I I I I I I I I I I I I CKY INC.. ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: 1310! 6 PHi818 I CKY QUALITY CONTROL DATA MS ANALYSIS IIILIENT: Ogden E~vironmental IIROJECT: Brandywine METHOD: EPA 310.1 MOISTURE: NAf TRIX: WATER BATCH NO.: 96B134 DATE RECEIVED: 02/28/96 PLE ID: MW05-SO~ DATE EXTRACTED: NA ONTROL NO.: B134-04 DATE ANALYZED: 03/01/96 ACCESSION: 96B134 IARAMETER llkalinity I I 1 I I I 1. I I I I I SMPL RSLT mg/L) SPIKE AMT mg/L) MS RSLT mg/L) MS QC LIMIT REC ( % ) 104.00 240.00 323.00 91 75-125 I ~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: t3 I 0) fl: S-liti 18 I CKY QUALITY CONTROL DATA LCS ANALYSIS IIENT: Ogden E~vironmental OJECT: Brandywine ETHOD: EPA 310.1 MOISTURE: NA TRIX: WATER . BATCH NO.: PLE ID: WJNTROL NO . : ACCESSION: IARAMETER llkalinity I I I I I I I I I I I I 96Bl34 LCSlW -- ALCOOlWL 96Bl34 BLNK RSLT SPIKE AMT mg/L) (mg/L) DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: LCS RSLT mg/L) LCS REC NA NA 03/01/96 QC LIMIT ND 152.00 142.00 93 85-115 CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .• Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 6i8-0818 I I I I I I I I I I I I I I I I I EPA METHOD 300 CHLORIDE CLIENT: PROJECT: BATCH NO.: MATRIX: Ogden Environmental Brandywine 96B134 WATER DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: 02/27/96 02/28/96 NA 03/06/96 RESULT DILUTION MDL SAMPLE ID -coNTROL NO (mg/L) FACTOR (mg/L) MWOl-SOl B134-01 4140 500 100 MW02-S01 B134-02 598 100 20 MW03-S01 B134-03 5400 1000 200 MW05-S01 B134-04 3330 500 100 MW04-S01 B134-05 2450 500 100 MBLKlW ICCOOlWB ND 1 .2 MDL : Method Detection Limit I ,~ CKY INC., ANALYTICAL lABORATORIES, 630 Maple Ave .• Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I CKY QUALITY CONTROL DATA DUPLICATE ANALYSIS I IENT: Ogden Environmental OJECT: Brandywine THOD: EPA 3DO MATRIX: WATER MOISTURE: NA . •----------------------------.--------------------------.---------------------- BATCH NO.: 96B134. DATE RECEIVED: 02/28/96 PLE ID: MW01-S01 DATE EXTRACTED: NA 9-1.NTROL NO.: B134-01 DATE ANALYZED: 03/06/96 ACCESSION: 96B134 LETER rloride I I I I I I I I I I I SAMPLE mg/L) DUP. SAMPLE mg/L) RPD RPD LIMIT 4140.00 4110.00 1 20 I I~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I CKY QUALITY CONTROL DATA LCS ANALYSIS I IENT: Ogden E~vironmental OJECT: Brandywine THOD: EPA 300 MOISTURE: NAJTRIX: WATER BATCH NO. : 96B134 DATE RECEIVED: NA PLE ID: LCSlW --DATE EXTRACTED: "NA NTROL NO.: ICCOOlWL DATE ANALYZED: 03/06/96 ACCESSION: 96B134 lRAMETER rloride BLNK RSLT mg/L) SPIKE AMT mg/L) LCS RSLT mg/L) LCS REC QC LIMIT ND 5.00 4.58 92 85-115 I I I I I I I I I I I I I CKY INC.. ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618·0~ 18 I I I I I I I I I I I I I I I I I EPA METHOD 300 SULFATE CLIENT: PROJECT: BATCH NO.: MATRIX: Ogden Environmental Brandywine 96B13.;I. WATER DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: 02/27/96 02/28/96 NA 03/06/96 RESULT DILUTION MDL SAMPLE ID -CONTROL NO (mg/L) FACTOR (mg/L) ----------------------------------------- MWOl-SOl B134-01 1800 100 100 MW02-S01 B134-02 358 100 100 MW03-S01 B134-03 1320 100 100 MW05-S01 B134-04 1020 100 100 MW04-S01 B134-05 1800 100 100 MBLKlW ICCOOlWB ND 1 1 MDL: Method Detection Limit I I~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: !3!Cn 1, l ,'l-i.,~ ! 8 I CKY QUALITY CONTROL DATA DUPLICATE ANALYSIS llr,IENT: Ogden E~vironmental 9ROJECT: Brandywine METHOD: EPA 300 TRIX: WATER MOISTURE: NA CH NO.: PLE ID: TROL NO.: ACCESSION: ARAMETER rlfate I I I I I I I I I I I I 96B134 DATE RECEIVED: 02/28/96 MWOl-SOl DATE EXTRACTED: NA B134-01 DATE ANALYZED: 03/06/96 96B134 SAMPLE mg/L) DUP. SAMPLE mg/L) RPD RPD LIMIT 1800.00 1790.00 1 20 I ~ CKY INC., ANALYTICAL LABORATORIES, 6.30 Maple Ave .. Torrance, Calif. 90503 Tel. (310) 618·8889 Fax: (310) 613·0818 I CKY QUALITY CONTROL DATA MS ANALYSIS IIENT: Ogden Environmental OJECT: Brandywine THOD: EPA 300 MATRIX: WATER MOISTURE: NA a======-----------------------.--------------------.-----=-------------======== BATCH NO.: 96B134 DATE RECEIVED: 02/28/96 PLE ID: MWOl-S01 DATE EXTRACTED: NA a-iNTROL NO.: B134-01 DATE ANALYZED: 03/06/96 ACCESSION: 96B134 lRAMETER rlfate I I I I I I I I I I I SMPL RSLT mg/L) SPIKE AMT mg/L) MS RSLT mg/L) MS REC QC LIMIT 1800.00 1000.00 3050.00 125 75-125 I ,~ CKY INC.. ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance, Calif. 90503 Tel. (310) 618·8889 Fax: (3 lOl 618-0818 I CKY QUALITY CONTROL DATA LCS ANALYSIS I IENT: Ogden Environmental OJECT: Brandywine METHOD: EPA 300 MOISTURE: NA · TRIX: WATER BATCH NO.: ltMPLE ID: a>NTROL NO.: ACCESSION: IRAMETER lfate I I I I I I I I I I 1 I 96B134 LCSlW -- ICCOOlWL 96B134 BLNK RSLT mg/L) SPIKE AMT mg/L) DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: LCS RSLT mg /L) LCS REC NA NA 03/06/96 QC LIMIT ND 10.00 8.80 88 85-115 I G<t CKY INC., ANALYTICAL lABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310l 618-0818 I I I I I I I I I I I I I I I I I I EPA METHOD 300 NITRATE CLIENT: PROJECT: BATCH NO.: MATRIX: Ogden Environmental Brandywine 96B13~ WATER DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: 02/27/96 02/28/96 NA 03/07/96 RESULT DILUTION MDL SAMPLE ID -eoNTROL NO (mg/L) FACTOR (mg/L) ----------------------------------------- MW01-S01 B134-01 5.91 25 2.5 MW02-S01 B134-02 17.4 25 2.5 MW03-S01 B134-03 231 100 10 MW05-S01 B134-04 8.57 10 1 MW04-S01 B134-05 228 100 10 MBLKlW ICC002WB ND 1 .1 MDL: Method Detection Limit I Get CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (3 lOl 1i 18-0818 I CKY QUALITY CONTROL DATA DUPLICATE ANALYSIS I IENT: Ogden E~vironmental OJECT: Brandywine METHOD: EPA 300 MOISTURE: NAI TRIX: WATER I CH NO.: PLE ID: NTROL NO.: ACCESSION: IRAMETER I I I I I I I I I I I I 96Bl34 DATE RECEIVED: 02/28/96 MWOl-SOl DATE EXTRACTED: NA Bl34-0l DATE ANALYZED: 03/07 /96 96Bl34 SAMPLE mg/L) DUP. SAMPLE mg/L) RPD RPD LIMIT 5.91 5.52 7 20 I Gv CKY INC., ANALYTICAL IABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618·8889 Fax: (3101 ii 1,.:,s 18 I CKY QUALITY CONTROL DATA MS ANALYSIS ILIENT: Ogden E~vironmental ROJECT: Brandywine METHOD: EPA 300 MOISTURE: NA. · [ TRIX: WATER BATCH NO.: 96B134 DATE RECEIVED: 02/28/96 IAMPLE ID: MW01-S01 DATE EXTRACTED: NA ONTROL NO.: B134-01 DATE ANALYZED: 03/07/96 ACCESSION: 96B134 ARAMETER litrate I I I I I I I I I I I SMPL RSLT mg/L) SPIKE AMT mg/L) MS RSLT mg/L) MS REC QC LIMIT 5.91 125.00 148.00 114 75-125 I I CKY INC., ANALYTICAL I.ABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I CKY QUALITY CONTROL DATA LCS ANALYSIS I IENT: Ogden E~vironmental OJECT: Brandywine METHOD: EPA 300 MOISTURE: NA · [ TRIX: WATER BATCH NO.: PLE ID: lf)NTROL NO. : ACCESSION: lRAMETER I I I I I I I I I I I 96B134 LCSlW -- ICC002WL 96B134 BLNK RSLT mg/L) SPIKE AMT mg/L) DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: LCS RSLT mg/L) LCS REC NA NA 03/07/96 QC LIMIT ND 5.00 5.10 102 85-115 I ,~ CKY INC.. ANALYTICAL IABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I I I, EPA METHOD 300 FLUORIDE CLIENT: PROJECT: BATCH NO.: MATRIX: Ogden Environmental Brandywine 96B134 WATER DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: 02/27/96 02/28/96 NA 03/07/96 RESULT DILUTION MDL SAMPLE ID ·coNTROL NO (mg/L) FACTOR (mg/L) ----------------------------------------- MWOl-SOl B134-01 .81 1 . 2 MW02-S01 B134-02 1.57 1 .2 MW03-S01 B134-03 .77 1 . 2 MWOS-SOl B134-04 .99 1 .2 MW04-S01 B134-05 .71 1 .2 MBLKlW FLCOOlWB ND 1 .2 MDL: Method Detection Limit I ~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I CKY QUALITY CONTROL DATA DUPLICATE ANALYSIS a:.IENT: Ogden Environmental OJECT: Brandywine METHOD: EPA 300 MOISTURE: NArTRIX: WATER BATCH NO.: 96B134 DATE RECEIVED: _02/28/96 PLE ID: MW03-S01 DATE EXTRACTED: NA 9-YNTROL NO.: B134-03 DATE ANALYZED: 03/07/96 ACCESSION: 96B134 lRAMETER ruoride SAMPLE DUP. SAMPLE RPD RPD LIMIT I I I I I I I I I I I I I~ mg/L) (mg/L) ( % ( % ) 77 .79 3 20 CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618·8889 Fax: 13 toJ 6 iS-0818 I CKY QUALITY CONTROL DATA MS ANALYSIS I IENT: Ogden Environmental OJECT: Brandywine METHOD: EPA 300 MOISTURE: NAITRIX: WATER ECH NO.: PLE ID: NTROL NO.: ACCESSION: LETER fuoride I I I I I I I I I I I 96Bl34 MW03-S01 Bl34-03 96Bl34 SMPL RSLT mg/L) SPIKE AMT mg/L) DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MS RSLT mg/L) MS REC 02/28/96 NA 03/07/96 QC LIMIT 77 5.00 5.16 88 75-125 I I~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618·8889 Fax: (31011, 1s.n~ 18 I CKY QUALITY CONTROL DATA LCS ANALYSIS 9r.IENT: Ogden Environmental OJECT: Brandywine METHOD: EPA 300 MOISTURE: NA [ TRIX: WATER ECH NO.: PLE ID: TROL NO.: ACCESSION: lRAMETER lluoride I I I I I I I I I I I I 96B134 LCSlW FLCOOlWL 96B134 BLNK RSLT mg/L) SPIKE AMT mg/L) DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: LCS RSLT mg/L) LCS REC NA NA 03/07/96 QC LIMIT ND 20.00 20.50 103 85-115 I · ~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 6 l8·08 l8 I I I I I I I I I I I I I I I I I EPA METHOD 150.1 PH CLIENT: PROJECT: BATCH NO.: MATRIX: Ogden Environmental Brandywine 96B134 WATER DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: 02/27/96 02/28/96 NA 03/01/96 RESULT DILUTION MDL SAMPLE ID ·coNTROL NO (pH unit) FACTOR (pH unit) ----------------------------------------- MWOl-SOl B134-01 7.4 1 .1 MW02-S01 B134-02 7.9 1 .1 MW03-S01 B134-03 7.3 1 .1 MWOS-SOl B134-04 7.3 1 .1 MW04-S01 B134-05 7.6 1 .1 MDL: Method Detection Limit I ,~ CKY INC., ANALYTICAL IABORATORIES, 630 Maple Ave., Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I CKY QUALITY CONTROL DATA DUPLICATE ANALYSIS I LI ENT: Ogden Environmental ROJECT: Brandywine METHOD: EPA 150.1 MOISTURE: NAf TRIX: WATER BATCH NO.: 96B134 DATE RECEIVED: 02/28/96 I AMPLE ID: MW05-S01. DATE EXTRACTED: NA ONTROL NO.: B134-04 DATE ANALYZED: 03/01/96 ACCESSION: 96B134 IARAMETER SAMPLE pH unit) DUP. SAMPLE pH unit) RPD RPD LIMIT I I I I I I I I I I I I I 7.30 7.30 0 20 CKY INC., ANALYTICAL lABORATORIES, 630 Maple Ave .. Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (3 lOl 618-0818 I CKY QUALITY CONTROL DATA LCS ANALYSIS I IENT: Ogden E~vironmental OJECT: Brandywine THOD: EPA 150.1 TRIX: _ WATER - MOISTURE: NA BATCH NO. : 96Bl34 DATE RECEIVED: NA PLE ID : LCS 1 W --DATE EXTRACTED: NA 91NTROL NO.: PHCOOlWL DATE ANALYZED: 03/01/96 ACCESSION: 96Bl34 LETER r I I I I I I I I I I I BLNK RSLT pH unit) ND SPIKE AMT pH unit) --------- 9.08 LCS RSLT pH unit) --------- 8.99 LCS REC QC LIMIT 99 85-115 I ,~ CKY INC., ANALYTICAL lABORATORIES, 630 Maple Ave .. Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: nto) 018-0818 I I I I I I I I I I I I I I I I I EPA METHOD 120.1 ELECTRICAL. CONDUCTIVITY CLIENT: PROJECT: BATCH NO.: MATRIX: Ogden Environmental Brandywine 96B134 · WATER DATE COLLECTED: DATE RECEIVED:. DATE EXTRACTED: DATE ANALYZED: 02/27/96 02/28/96 NA 03/04/96 RESULT DILUTION MDL SAMPLE ID ·toNTROL NO (umhos/cm) FACTOR (umhos/cm) ----------------------------------------- MWOl-SOl B134-01 11900 1 .5 MW02-S01 B134-02 3720 1 .5 MW03-S01 B134-03 16700 1 .5 MW05-S01 B134-04 9740 1 .5 MW04-S01 B134-05 10800 1 .5 MDL: Method Detection Limit I ,~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave., Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: !3 !Oi 11 t s-D!:l 18 I CKY QUALITY CONTROL DATA DUPLICATE ANALYSIS ILIENT: Ogden E~vironrnental OJECT: Brandywine METHOD: EPA 120.1 MOISTURE: NA [ TRIX: . WATER ·· -- BATCH NO.: 96B134 DATE RECEIVED: 02/28/96 PLE ID: MWOl-SOl DATE EXTRACTED: NA IJ)NTROL NO.: B134-01 DATE ANALYZED: 03/04/96 ACCESSION: 96B134 lRAMETER SAMPLE urnhos/crn) DUP. SAMPLE urnhos/crn) RPD RPD LIMIT 11ectrical Conductivity I I I I I I I I I I I I 11900.00 11900.00 0 20 I ~ CKY INC.. ANALYTICALLABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310i Al8-1)8!8 I CKY QUALITY CONTROL DATA LCS ANALYSIS ar,IENT: Ogden Environmental OJECT: Brandywine METHOD: EPA 120 .1 _ _ __ . MOISTURE : NA r· TRIX: ----WATER --- ECH NO.: PLE ID: TROL NO.: ACCESSION: lRAMETER 96B134 LCSlW -· ECCOOlWL 96Bl34 DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: BLNK RSLT SPIKE AMT LCS RSLT umhos/cm) (umhos/cm) (umhos/cm) LCS REC rectrical Conductivity ND 1410.00 1410.00 100 NA NA 03/04/96 QC LIMIT 85-115 I I I I I I I I I I I I I CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave., Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I 1 I I I I I I I I I I I I I I EPA METHOD 160.1 TOTAL DISSOLVED SOLIDS CLIENT: PROJECT: BATCH NO.·: MATRIX: Ogden Environmental Brandywine 96B134 WATER DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: 02/27/96 04/28/96 NA 03/04/96 RESULT DILUTION MDL SAMPLE ID -CONTROL NO (mg/L) FACTOR (mg/L) ----------------------------------------- MWOl-SOl Bl34-01 7900 1 10 MW02-S01 Bl34-02 2310 1 10 MW03-S01 Bl34-03 10600 1 10 MW05-S01 Bl34-04 5800 1 10 MW04-S01 Bl34-05 7820 1 10 MBLKlW DSCOOlWB ND 1 10 MDL : Method Detection Limit I I~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I CKY QUALITY CONTROL DATA DUPLICATE ANALYSIS I IENT: Ogden E~vironmental OJECT: Brandywine ETHOD: EPA 160.1 MOISTURE: NAiATRIX: .. . WATER · · · · . .. BATCH NO.: PLE ID: SJNTROL NO. : ACCESSION: IARAMETER rs I I I I I I I I I I I 96B134 TURBDT/TDS-SPS C016-08 96B134 96C015 96C016 SAMPLE DUP. SAMPLE mg/L) (mg/L) DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: RPD NA NA 03/04/96 RPD LIMIT 915.00 980.00 7 20 I I~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I CKY QUALITY CONTROL DATA LCS ANALYSIS I IENT: Ogden E~vironmental OJECT: Brandywine METHOD: EPA loO.l . MOISTURE: NA rTRIX: · WATER . . . ACCESSION: IRAMETER I I I I I I I I I I I I 96Bl34 DATE RECEIVED: NA LCSlW DATE EXTRACTED: NA DSCOOlWL DATE ANALYZED: 03/04/96 96Bl34 96C015 96C016 BLNK RSLT SPIKE AMT LCS RSLT mg/L) (mg/L) (mg/L) LCS REC QC LIMIT ND 856.00 770.00 90 85-115 I ~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618·8889 Fax: (3 lOi bl~ •.1:-l 18 I I I I I I I I I I I I I I I I I EPA 110.2 COLOR CLIENT: PROJECT: BATCH NO.: MATRIX: Ogden Environmental Brandywine 96B134 ··· WATER DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: 02/27/96 02/28/96 · NA 02/29/96 ==========================~========================================= RESULT DILUTION MDL SAMPLE ID CONTROL NO (Color Units) FACTOR (Color Units) ----------------------------------------- MWOl-SOl B134-01 10 1 10 MW02-S01 B134-02 10 1 10 MW03-S01 B134-03 40 1 10 MW05-S01 B134-04 10 1 10 MW04-S01 B134-05 40 1 10 MBLKlW COBOOlWB ND 1 10 MDL : Method Detection Limit I ,~ CKY INC .• ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (3 lOl 618-08 t 8 I CKY QUALITY CONTROL DATA DUPLICATE ANALYSIS IIENT: Ogden E~vironmental OJECT: Brandywine ETHOD: EPA 110.2 MOISTURE: NArTRIX: WATER ·· · . BATCH NO.: 96B134 DATE RECEIVED: 02/28/96 PLE ID: MW04-S01 DATE EXTRACTED: NA a:,>NTROL NO.: B134-05 DATE ANALYZED: 02/29/96 ACCESSION: IARAMETER rlor 96B134 SAMPLE DUP. SAMPLE Color Units) (Color Units) 40.00 40.00 RPD 0 RPD LIMIT 20 I I I I I I I I I I I I I CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I CKY QUALITY CONTROL DATA LCS ANALYSIS IILIENT: Ogden Environmental IIIIR.OJECT: Brandywine METHOD: EPA 110.2 MOISTURE: NArTRIX: WATER BATCH NO.: IAMPLE ID: ONTROL NO.: ACCESSION: IARAMETER 96B134 LCSlW -- COBOOlWL 96B134 BLNK RSLT SPIKE AMT Color Units) (Color Units) ND 30.00 DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: LCS RSLT LCS Color Units) % REC 30.00 100 NA NA 02/29/96 QC LIMIT 85-115 I I I I I I I I I I I I I CKY INC., ANALYTICAL IABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 TeL (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I I I I EPA 140.1 ODOR CLIENT: PROJECT: BATCH NO.: MATRIX: Ogden Environmental Brandywine 96B13-4 WATER. DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: 02/27/96 02/28/96 NA 02/29/96 RESULT DILUTION MDL SAMPLE ID ·CONTROL NO (TON) FACTOR (TON) ----------------------------------------- MWOl-SOl B134-01 ND 1 1 MW02-S01 B134-02 ND 1 1 MW03-S01 B134-03 ND 1 1 MWOS-SOl B134-04 ND 1 1 MW04-S01 B134-05 ND 1 1 MBLKlW ODBOOlWB ND 1 1 MDL : Method Detection Limit G\, CKY INC.. ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 6 l 8-il818 I CKY QUALITY CONTROL DATA DUPLICATE ANALYSIS I IENT: Ogden Environmental OJECT: Brand~ine METHOD: EPA 140.1 MOISTURE: NA [ TRIX: WATER I CH NO.: PLE ID: NTROL NO.: Z\CCESS ION: lRAMETER I I 96B134 DATE RECEIVED: 02/28/96 MWOl~SOl DATE EXTRACTED: NA B134-01 DATE ANALYZED: 02/29/96 96B134 SAMPLE TON) DUP. SAMPLE TON) RPD RPD LIMIT ND ND O 20 I I I I I I I I I I I CKY INC., ANALYTICAL LABORATORIES. 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: 13101 61 s-nR 18 I I I I I I I I I I I I I I I I I I I EPA METHOD 130.2 TOTAL HARDNESS CLIENT: PROJECT: BATCH NO.: MATRIX: Ogden Environmental Brandywine 96B13<l WATER DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: 02/27/96 02/28/96 NA 03/05/96 =============================-====================================== RESULT DILUTION MDL SAMPLE ID -coNTROL NO (mg/L) FACTOR (mg/L) ----------------------------------------- MWOl-SOl B134-01 3960 1 10 MW02-S01 B134-02 337 1 10 MW03-S01 B134-03 3320 1 10 MW05-S01 B134-04 2500 1 10 MW04-S01 B134-05 1880 1 10 MBLKlW IPCOOlWB ND 1 10 MDL: Method Detection Limit G\, CKY INC., ANALYTICAL lABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (3 lOi 618-0818 I I IENT: Ogden Environmental OJECT: Brandywine METHOD: EPA 130.2 MOISTURE: NA CKY QUALITY CONTROL DATA LCS/LCD ANALYSIS ITRIX: WATER ITCH NO.: MPLE ID: NTROL NO.: ACCESSION: lRAMETER Ital Hardness I I I I I I I I I I I 966134 LCS1W/LCS1WD IPC00111L/C 966134 BLNK RSLT SPIKE.AMT BS RSLT mg/L) (mg/L) (mg/L) BS REC DATE RECEIVED: NA DATE EXTRACTED: NA DATE ANALYZED: 03/05/96 SPIKE AMT BSD RSLT Cmg/L) (mg/L) BSD REC RPD QC LIMIT RPD LIMIT ND 331.00 334.00 101 331.00 319.00 97 5 85-115 20 I I~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 w ... g c 00 00 w w ... . s 6 00 ... 00 SAMPLE RECEIPT FORM CONTROL NO. 96BJ3 '-/ DATE 02-")~ -96 I CLIENT ' Ol,(.))@\J, 8)VI ,:., ;J • TIME Ille:> PROJECT B M-IJ 'IY4 WI "1 ~ RECIPIENT ~.f)Rr£L__ I I SAMPLE TRANSPORTATION TO CKY LABORATORY: BY ON(DATE) AT(TIME) FROM(SITE/CO.l COMMENTS PICKED-UP BY CKY COURIER DELIVERED BY CLIENT ~ SHIPPED/AIRBILL NO A-fV\ f'M '.b~· -# &f-O :L.~7(:. u:: LO I ~f: ~"::( f:U ,. SAMPLE BATCH PACKAGING/SEALING UPON RECEIPT: NO CONTAINER .,.......INTACT DAMAGED NOT SEALED tt" SEALED CONTAINER: INSIDE TEMPERATURE: 3"' C CUSTODY SEAL /OTHER SEAL LOCATION NUMBER 2-COOLER.> PACKAGING TYPE SUFFICIENCY .,.....-INTACT DAMAGED Fl(.DNT""e..t.1114U" ')... BOX INSULATION: t1U-NAME: Q~C.-C.. i..£'AfLUOl "'-fL! ( OTHER: ICE/COOLANT: ~·u l.lt1l--1 · · DATE: .-~ . LPACKINGMATERIAL: / TIME: SAMPLE DOCUMENTATION/CHAIN-OF-CUSTODY(COC) NONE / HANDCARRIED ENCLOSED FAXED SEALED I SAMPLE LOG-IN: CRITERIA COMMENTS DISCREPANCY .• SAMPLE CUSTODY SEAL EVERY SAMPLE NING" CONTAINER TYPE/MATERIAL APPROPRIATE C1L-_/"' SAMPLE AMOUNT ENOUGH / SAMPLE PRESERVATION/HOLDING TIME SUFFICIENT / HEADSPACE/BUBBLES ZERO/NONE / SAMPLE LABEL INFORMATION SUFFICIENT / CHAIN-OF-CUSTODY INFORMATION SUFFICIENT 1 .. / SAMPLE INFO.: SAMPLE ID ,-DATE -TIME r-SIGNATURE .,. ANALYSES -l"" PRESERVATIVE .,t-· CONTAINER ,,,... INDIVIDUAL SAMPLE CONTAINER: .;""'fJONE PLASTIC BAG ·CAN OTHER(SPECIFY): SEALED 1 SAMPL.E NUMBER CLIENT ID DISCREPANCY ACTION .,, i ./ ./ ./ I ·/ _...-./ V, \ ./"' / 7 7 7 V /'\ -.. , . /-, r-· ' .,,,7 .~, - CLIENT SERVICES COPY RECEIVED BY c . v L-c UY--./ '-' I vo I DATE TIME I I I I I I I I I I I I I I I I I I I I Date: 03-13-1996 CKY Batch No.: 96B134 Attn: Don Barrie Ogden Environmental 5510 Morehouse Drive San Diego, CA 92121 Subject: Laboratory Report Project: Brandywine C K Y incorporated Analytical Laboratories Enclosed is the Laboratory report for samples received on 02/28/96. The samples were received in coolers with ice and intact; the chain-of-custody forms were properly filled out. The data reported include : Sample ID Control No. Matrix Analysis MWOl-.SOl B134-01 Water MW02-S01 B134-02 Water EPA 8010 EPA 8020 Metals Mercury MBAS Turbidity Alkalinity Sulfate Chloride Fluoride g~nductivity TDS Color Odor Total Hardness Nitrate EPA 8010 EPA 8020 I 630 Maple Ave., Torrance, Calif. 90503 • Telephone 310-618-8889 • Fax: 310-618-0818 I I I I I I I I I I I I I I I I I I I G\, Sample ID Control No. MW03-S01 B134-03 MWOS-SOl B134-04 Matrix Analysis Metals Mercury MBAS Turbidity Alkalinity Sulfate Chloride Fluoride g~nductivity TDS Color Odor Total Hardness Nitrate Water EPA 8010 EPA 8020 Metals Mercury MBAS Turbidity Alkalinity Sulfate Chloride Fluoride g~ndactivity TDS Color Odor Total Hardness Nitrate Water EPA 8010 EPA 8020 Metals Mercury MBAS Turbidity Alkalinity Sulfate Chloride CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I I I I ~ Sample ID Control No. MW04-S01 B134-05 Matrix Analysis Fluoride g~nductivity TDS Color Odor Total Hardness Nitrate Water EPA 8010 EPA 8020 Metals Mercury MBAS Turbidity Alkalinity Sulfate Chloride Fluoride g~nductivity TDS Color Odor Total Hardness Nitrate The results are summarized on the following pages. Please feel free to call if you have any questions concerning these results. Sincerely yours, Kam Y. Pang, Ph.~. Laboratory Director P.S. -All analyses requested for the above referenced project have been completed. Therefore, unless instructed, the remaining portions of the samples will be disposed after fifteen (15) days from the date of this report. CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618·8889 Fax: (31()\ 618-0818 I I I I I I I I I I I I I I I I I I I Febru~ry 28, 1996 CLIENT: OGDEN GENERAL MINERALS LIST MBAS, Turbidity, Alkalinity, Sulfate, Chloride, Fluoride, pH, Electrical Conductivity, TDS, Color, Odor, Hardness, Nitrate. Aside from CAM Metals (17 metals) client also requests the following elements: Calcium, Magnesium, Sodium and Potassium. ·· I I I I I I I I I I I I I I I I I I ,~ EPA METHOD 3005/6010 METALS BY ICP CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO . : MOISTURE: Ogden Environmental Brandywine 96B13~ MWOl-SOl B134-01 NA DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: 02/27/96 02/28/96 03/01/96 03/04/96 WATER 1 Element Antimony Arsenic Barium Beryllium Cadmium Calcium Chromium Cobalt Copper Leaa Magnesium Molybd~num Potassium Nickel Selenium Silver Sodium" Thallium Vanadium Zinc Det Limit ug/L) 60 100 10 5 5 1000 10 10 10 100 1000 50 2000 20 200 10 2000 500 10 10 A Analyzed on 03/05/96 at 2x dilution. RESULT ug/L) ND ND 284 ND ND 791000 67.7 16.4 51 ND 481000 73.9 40100 37.5 ND ND 1110000 ND 115 440 CKY INC.. ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: \3101 618-0H 18 I I I I I I I I I I I I I I I I I I ,~ EPA METHOD 3005/6010 METALS BY ICP CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO. : MOISTURE: Ogden Environmental Brandywine 96B134 MW02-S01 B134-02 NA DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: 02/27/96 02/28/96 03/01/96 03/04/96 WATER 1 Element Antimc;my Arsenic Barium Beryllium Cadmium Calcium Chromium Cobalt Copper Leaa Magnesium Molybd~num Potassium Nickel Selenium Silver SodiumA Thallium Vanadium Zinc Det Limit ug/L) 60 100 10 5 5 1000 10 10 10 100 1000 50 2000 20 200 10 2000 500· 10 10 A Analyzed on 03/05/96 at 2x dilution. RESULT ug/L) ND ND 37.8 ND ND 79800 ND ND ND ND 33400 ND 3670 ND ND ND 605000 ND 29.1 38.4 CKY INC., ANALYTICAL lABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 6!8·0818. I I I I I I I I I I I I I I I I I I EPA METHOD 3005/6010 METALS BY ICP CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO . : MOISTURE: Ogden Environmental Brandywine 96B134 MW03-S01 B134-03 NA DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: 02/27/96 02/28/96 03/01/96 03/04/96 WATER 1 Element Antimony Arsenic Barium Beryllium Cadmium Calcium Chromium Cobalt Copger Leaa Magnesium Molybd~num Potassium Nickel Selenium Silver SodiumA Thallium Vanadium Zinc Det Limit ug/L) 60 100 10 5 5 1000 10 10 10 100 1000 50 2000 20 200 10 10000 500 10 10 A ·Analyzed on 03/05/96 at lOx dilution. RESULT ug/L) ND 171 762 ND ND 725000 266 111 129 158 366000 ND 62700 325 ND ND 268000 1440 647 1290 I ~ CKY INC., ANALYTICAL lABORATORIES, 630 Maple Ave., Torrance, Calif. 90503 Tel. (310) 618·8889 Fax: (310) 618-0818 I I I I I I I I I I I I I I I I I I ,~ EPA METHOD 3005/6010 METALS BY ICP CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO. : MOISTURE: Ogden Environmental Brandywine 96Bl34 MW05-S01 Bl34-04 NA DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: 02/27/96 02/28/96 03/01/96 03/04/96 WATER 1 Element Antimc;my Arsenic Barium Beryllium Cadmium Calcium Chromium Cobalt Copper Leaa. Magnesium Molybd~num Potassium Nickel Selenium Silver SodiumA Thallium Vanadium Zinc Det Limit ug/L) 60 100 10 5 5 1000 10 10 10 100 1000 50 2000 20 200 10 5000 500 10 10 A Analyzed on 03/05/96 at 5x dilution. RESULT ug/L) ND 303 1480 6.41 ND 519000 701 160 255 230 291000 ND 114000 182 3590 ND 1380000 2540 1010 4220 CKY INC.. ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503Tel. (310) 618-8889 Fax: \310) 618·08i8 I I I I I I I I I I I I I I I I I I I G\, EPA METHOD 3005/6010 METALS BY ICP CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO . : MOISTURE: Ogden Environmental Brandywine 96Bl34 MW04-S01 B134-05 NA DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: 02/27/96 02/28/96 03/01/96 03/04/96 WATER 1 Element Antimc;my Arsenic Barium Beryllium Cadmium Calcium Chromium Cobalt Copger Leaa Magnesium MolybdE?num Potassium Nickel Selenium Silver SodiumA Thallium Vanadium Zinc Det Limit ug/L) 60 100 10 5 5 1000 10 10 10 100 1000 50 2000 20 200 10 5000 500 10 10 A Analyzed on 03/05/96 at 5x dilution. RESULT ug/L) ND ND 196 ND ND 433000 54.3 36.9 30.1 ND 195000 ND 21400 217 ND ND 1620000 ND 111 482 CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618·8889 Fax: (310) Ii 1,,.,1:-s iS I I I I I I I I I I I I I I I I I I I~ EPA METHOD 3005/6010 METALS BY ICP CLIENT: PROJECT: BATCH NO.: SAMPLE ID: CONTROL NO. : MOISTURE: Ogden Environmental Brandywine 96Bl34 MBLKlW IPCOOlWB NA DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: MATRIX: DILUTION FACTOR: NA NA 03/01/96 03/04/96 WATER 1 Det Limit RESULT Element (ug/L) (ug/L) Antimc;my 60 ND Arsenic 100 ND Barium 10 ND Beryllium 5 ND Cadmium 5 ND Calcium 1000 ND Chromium 10 ND Cobalt 10 ND Cop~er 10 ND Lea 100 ND Ma 1nesium 1000 ND Mo ybd~num so ND Potassium 2000 ND Nickel 20 ND Selenium 200 ND Silver 10 ND SodiumA 1000 ND Thallium 500 ND Vanadium 10 ND Zinc 10 ND A Analyzed on 03/05/96 CKY INC., ANALYTICAL LABORATORIES. 630 Maple Ave .. Torrance, Calif. 90503 Tel. (310) 618·8889 Fax: (3101 6 I 8-0818 I CKY QUALITY CONTROL DATA DUPLICATE SAMPLE ANALYSIS I IENT: Ogden Environmental OJECT: Brandywine METHOD: EPA 3005/6010fTRIX: WATER . BATCH NO.: 96B134 DATE RECEIVED: NA . SAMPLE ID: PW-Ll/2/3 DATE EXTRACTED: 03/01/96 ia)NTROL NO.: 0202-02· DATE ANALYZED: 03/04/96 CESSION: N960202 96B134 I PARAMETER 1--;----.--timony senic Barium l rytlium dmium lcium Chromium l balt er agnesium Molybdenum l tassium ckel lenium Silver l diumA allium nadium Zinc I LIMIT: Analyzed on 03/05/96 Outside the QC limit I I I I I I SAMPLE RESULT ug/L) ND ND 60.2 ND ND 30300 ND ND 64 ND 5250 ND 44900 21 ND ND 178000 ND ND 601 DUP SAMPLE RESULT ug/L) ND ND 61.1 ND ND 31000 ND ND 63.7 ND 5340 ND 43000 39.9 ND ND 171000 ND ND 612 RPD RESULT 0 0 1 0 0 2 0 0 0 0 2 0 4 62+ 0 4 0 0 2 20 I I~ CKY INC., ANALYTICAL lABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: !310) 618-08 i 8 I CKY QUALITY CONTROL DATA SPIKE ANALYSIS I IENT: Ogden Environmental OJECT: Brandywine THOD: EPA 3005/6010 x~~~:=======::~::======= ===========~:;;=;;~;;~;~:===;:=================== SAMPLE ID: PW-Ll/2/3 DATE EXTRACTED: 03/01/96 lf)NTROL NO.: 0202-02-DATE ANALYZED: 03/04/96 l:cESSION: N960202 96B134 LETER SAMPLE RESULT ug/L) --------------- 1tim9ny ND sen1.c ND rium 60.2 Beryllium NDldmiumND lcium 30300 romium ND obalt ND Co~~er 64 ND lrnesium 5250 kbdenum ND Nie el 21 ltassium 40100 lenium ND lver ND SodiumA 178000 lallium ND nadium ND nc 601 Analyzed on 03/05/96I LIMIT: I I I I I I I SPIKE CONC. ug/L) ------ 5000 1000 1000 1000 1000 50000 1000 1000 1000 1000 50000 1000 1000 50000 1000 1000 50000 1000 1000 1000 SPIKE RESULT ug/L) 5060 1120 1020 981 1020 82400 1010 1010 1050 1020 52900 1010 1040 87670 997 1040 213000 918 1000 1640 SPIKE RECRY. 101 112 96 98 102 104 101 101 99 102 95 101 102 95 100 104 - 71 92 100 103 75-125 I G<t CKY INC.. ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (3 lOi 6 !S-0818 I CKY QUALITY CONTROL DATA LABORATORY CONTROL SAMPLE ANALYSIS I IENT: Ogden E~vironmental OJECT: Brandywine METHOD: EPA 3005/6010fTRIX: WATER . . _ BATCH NO. : 96B134 DATE RECEIVED: NA . IAMPLE ID: LCS1W/LCS1WD DATE EXTRACTED: 03/01/96 NTROL NO.: IPCOOlWL/C DATE ANALYZED: 03/04/96 CESSION: N960202 96B134 I SAMPLE SPIKE LCS SPIKE LCSD CONC ADDED CONC LCS ADDED CONC LCSD PARAMETER (ug/L) (ug/L) (ug/L) % REC (ug/L) (ug/L) % REC % RPD1-~----------------------- ------------------------------t1mony ND 5000 5090 102 5000 4909 98 4 senic ND 1000 1010 101 1000 1008 101 0 Barium ND 1000 1012 101 1000 978 98 3 lryllium ND 1000 1032 103 1000 987 99 5 dmium ND 1000 999 100 1000 946 95 5 lcium ND 50000 52316 105 50000 48247 96 8 Chromium ND 1000 1057 106 1000 986 99 7lbaltND100010321031000983985 er ND 1000 946 95 1000 939 94 1 ND 1000 991 99 1000 1013 101 2 arnesium ND 50000 49468 99 50000 48321 97 2 Mo ybdenum ND 1000 1040 104 1000 990 99 5 1tassium ND 50000 46577 93 50000 46542 93 0 ckel ND 1000 1031 103 1000 967 97 6 lenium ND 1000 1073 107 1000 983 98 _ 9 Silver ND 1000 1013 101 1000 970 97 4 ldiumA ND 50000 46854 94 50000 47138 94 1 allium ND 1000 934 93 1000 987 99 5 nadium ND 1000 1036 104 1000 976 98 6 Zinc ND 1000 1020 102 1000 976 98 4 I LIMIT: 75-125 75-125 20 Analyzed on 03/05/96 I I I I I I I I~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-01118 I I I I I I I I I I I I I I I I I EPA METHOD 7470 MERCURY BY COLD VAPOR CLIENT: PROJECT: BATCH NO.: MATRIX: Ogden Environmental Brandywine · 96B134 WATER DATE COLLECTED: DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: 02/27/96 02/28/96 03/07/96 03/07/96 RESULT DILUTION MDL SAMPLE ID ·CONTROL NO (ug/L) FACTOR (ug/L) ----------------------------------------- MWOl-SOl B134-01 ND 1 .2 MW02-S01 B134-02 ND 1 .2 MW03-S01 B134-03 .54 1 .2 MW05-S01 B134-04 5.13 1 .2 MW04-S01 B134-05 .28 1 . 2 MBLKlW HGC004WB ND 1 . 2 MDL: Method Detection Limit I I~ CKY INC., ANALYTICAL LABORATORIES. 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: 1.3101 61 :,-u>< 18 I CKY QUALITY CONTROL DATA DUPLICATE ANALYSIS lrIENT: Ogden Environmental OJECT: Brandywine METHOD: EPA 7470 MOISTURE: NAIATRIX: WATER IATCH NO.: AMPLE ID: ONTROL NO.: CCESSION, PARAMETER lercury I I I I I I I I I I I I 96B134 HA0003S0001EB C004-01 96B121 96B134 96C004 SAMPLE ug/L) DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: 96C011 DUP. SAMPLE RPD ug/L) ( % NA 03/07/96 03/07/96 RPD LIMIT ND ND O 20 I ~ CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: !310i 618-0818 I CKY QUALITY CONTROL DATA MS ANALYSIS ILIENT: Ogden Environmental ROJECT: Brandywine METHOD: EPA 7470 TRIX: WATER . MOISTURE: NA . BATCH NO.: 96B134 DATE RECEIVED: NA AMPLE ID: HA0003S0001EB DATE EXTRACTED: 03/07/96 ONTROL NO.: C004-01 DATE ANALYZED: 03/07/96 ACCESSION: 96B121 96B134 96C004 96C011 l SMPL RSLT SPIKE AMT MS RSLT MS QC LIMIT ARAMETER (ug/L) (ug/L) (ug/L) % REC ( % ) rercury I I I I I I I I I I I I I ND 5.00 4.76 95 75-125 CKY INC., ANALYTICAL lABORATORIES, 630 Maple Ave .. Torrance, Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618·0818 I CKY QUALITY CONTROL DATA LCS ANALYSIS LIENT: Ogden E~vironmental 9ROJECT: Brandywine METHOD: EPA 7~70 MOISTURE: NA [ TRIX: WATER BATCH NO.: PLE ID: ONTROL NO . : ACCESSION: IARAMETER lercury I I I I. I I I I· I I I 96Bl34 LCSlW -- HGC004WL 96Bl21 96Bl34 96C004 96C011 BLNK RSLT SPIKE AMT ug/L) (ug/L) DATE RECEIVED: DATE EXTRACTED: DATE ANALYZED: LCS RSLT ug/L) LCS REC NA 03/07/96 03/07/96 QC LIMIT ND 5.00 5.05 101 75-125 I I CKY INC., ANALYTICAL LABORATORIES, 630 Maple Ave .. Torrance. Calif. 90503 Tel. (310) 618-8889 Fax: (310) 618-0818 Rl:C31tB134 ' Al :~ .......... :. ·--: .. CLIENT O°'"' ~ , ~CHAIN OF CUSTODY RECORD I NAME: -~ \\\.._~\\\){'\fuf> REQUEST.FOR ANALYSIS ~ CK Yi•ro,j,oroled • ADDRESS: ~~ \ (""'\ MnrP V'\ci \.~ ~ or DATE: d-?,3:-C\ l,o Analytical Laborato~~ T°',,,, \ e Cl. ~ (" ~ C\ '"'2. _\ 7 \ PAGE_l_ OF 630 Maple Ave. . , '\ ·- Torrance, Calif. 905r. . · _ · ·-· PHONE Nd_~,..l(l:u~-~\J~ NO~\Q ~ :::09\.\3 Tel: 310-618-8889 . /. PROJECTNAME: ~~~ -' f'ax: 310-618-0818 ·. I SENOREPORTTO:~;;;~.,i> · -- TURN AROUf.lD TIME ANALYSES ~UIBED y SAMPLER NAME/SIGNATURE ~~~~---NORMAL --' -tJ\. ~,~r-0 "' D. --j 1 ~~lJ ·•··· RUSH D I C\I ~ 'I' II) ,·· I C\I II) ~ : E g s·:,. SAMPLE SAMPLING PRESER, CONTAINER -I ; iSAMPLEDESCRIPTIONco 2 ,... !f/JcDzNUMBERDATE/TIME SIZE/TYPE -~ ~ VATIVE WATER SOIL OTl'IBR. 'I' , ~ l\.~\()\-~ \ ")-~A~ -Urn X \ '3 -z.. \ 2--M,~-i'_-S) \ ~-:n..Q~ . \lt\\5' y:.. ' 3 2. I 3 M\No3-~\ :::l-".:n n~ ·-r-\45 'I:. l 3 z. ' L/ 'N\. \1\.\ c~ -~ I ~,t;A-<l'S \a.t-o X ' ~ 2 I r M.WD4-::Cf d'~":.\-C\5 \Q~ )( ( ~ '2.. I 1 I'<("\ '"''~ ~\4v.)I ~~t)3 ~ '~" °'" \e.. 1 \,V'\ ,~ ~00'°'-\ ~'i COMMENTS: ~Q \O\ ~'2.0 \. N'\ "'3."" t) "" \ \l C) f'r . VI"\ \-\ Z. <:,C '-f . F,..,r ~. . M. '"' \ ('\ "'l "I. \ ~ Oo\" -'-• "'-<l ...n ,f\ " ~ A ont. ~ <::.J\.. \"¥\. (""'\ \ p I 1 l tl. ,. l e~: _(nature) I ~~:i\ . aL. ~~~· ~ --~/2~£ Relin~~~e) -·-·, Date: R~ 1 nature) --tTut·cd Company: Time: ~~ ;m;1> ~~~ Time:~ OOapa~;/ Time: Oo...~" 2o'4~ ///C> II I o ' Stora~is osal of Sample.s: Sample will be stored at CKY for 30 days at no charge and at $10/sample/month thereafter. Disposal of sample b the Laborator wilr be char ed at $10/sam le. g p y y g p r I I I I I I I I I I I ,. I. I I I I I. I CALIFORNIA REGIONAL WATER QUALITY CONTROL BOARD LOS ANGELES REGION LABORATORY REPORT FORM Laboratory Name: CKY. Incorporated Address: 630 Maple Avenue, Torrance, CA 90503 Telephone (310) 618-8889 Laboratory Certification ELAP)No.: 1111 Expiration Date: 02/29/96 Laboratory Director's Name (Print): Kam Y. Pang, Ph.D. Laboratory Director's Signature: Client: Ogden Environmental Project No.: Chula Vista Analytical Method: EPA502.1 EPA503.1 EPA502.2 Circle One) EPA601 EPA602 EPA801V @s02v EPA8021 Other: Date Sa~pled: 02/10/96 02/10/96 Date Received: 02/12/96 02/12/96 Date Reported: 02/12/96 02/12/96 to 02/13/96 to 02/14/96 Sample Matrix: Soil Soil Extraction Method: Extraction Material: Chain of Custody Received: ® No Sample Condition . Sample Headspace Description (% ): Sample Container Materials: I EPA524.1 EPA524.2 EPA624 EPA8240 EPA8260 I I I ug/L I ;f~~~filf/i:i£~:r~~~= oz;-% 1 ::i:1:::::::::;;1,:1::::i::::::ii::::1:::::::::::1:::::ii:::i::i::11:::1::iii::::::i::;:::::::11:::1::11:1:: 1!: 1:1::i:i:!:11:::!:::i:!:11:!:1:1:i:::1:1:1:!~:::11:::::111:!1111::::11:11::~i:~w:g~:;1::i:i::111::i: BOf~-o, 1 JiH:\t'@fllffff:II:!\:::tt:f+I:;fffitfTTf'M!lfa¢.LlEITT:i$AMPLE.':iit5ttf:: N~1Dto.o I :'\'{'.t}c6MP:oONb'Y6ifli}W?tt1:\t'ttt@lWI{%HtiHHW:t:ft:)tttl ltMbtN@t ll?M.13\1%:t :c:am::uattt:::=-~ Bromobenzene I I Bromodichloromethane I Bromoform I Bromomethane I I Carbon tetrachloride I Chloroethane I Chloroform --.·. I I 1 -Chlorohexane I Chloromethane I Dibromochloromethane I Dibromomethane Dichlorodifluoromethane 1, 1-Dichloroethane (1, 1-DCA) 1 1,2-Dichloroethane (1,2-DCA) I I 1, 1-Dichloroethylene (1, 1-DCE) I I Itrans-1,2-Dichloroethylene I IIDichloromethane . I I 1,2-Dichloropropane I I I I cis-1,3-Dichloropropylene I I I trans-1,3-Dichloropropylene I ·1 I 1, 1, 1,2-Tetrachloroethane I I · ,~-----------,- h---------1 ---------1-------,1 ··I 1, 1,2,2-Tetrac loroethane Tetrachloroethylene (PCE) .I I I 1, 1, 1-Trichloroethane (111 _:TCA) I I I I 1,1,2-Trichloroethane(112-TCA) I I\ T_ri_ch_lo_r_o_et_hyL...l_en_e_(,_T_C_E...___) _______ ;--__ .,__ __ +-----+-----+-1-----,1 11,2,3-Trichloropropane I I ITrichlorofluoromethane I I Vinvl chloride I I Benzene s.11-'t ND I IIChlorobenzeneII 1,2-Dichlorobenzene I I 1,3-Dichlorobenzene I I 1,4-Dichlorobenzene I I IEthyl benzene S'.4-'1 ND I IIToluene5,'f't ND I I I I I I I I I I I 1· I I I I ANALYTICAL TEST RESULT (con rd) 1 · .... },,:·<:;:::::co MPOUND::'(b)\')tt=::ttt?f#%t=f't::f:J,,\:}'(}{f?(t}b{MDbt/} '\i/MB)@'{ hJJ\6.t):,'t{:1=,f:C)}}ttt>rl::t:::rr::{?}::r ii lm,p-Xylenes I I I I ITotcJIXylenesI16. 5' I ND I I Acetone I I I Acrolein I I I I Acrylon itrile I I I I Bromochloromethane I I I n -Butylbenzene I .I I sec-Butylbenzene I I I I I Itert-Butylbenzene I I I I ,, I, 2-Chloroethylvinyl ether I I I I ii 2-Chlorotoluene I I I I I Ii I4-Chlorotoluene I . ·.:. I I I I llIDichlorodifluoromethaneIIII cis-1,2-Dichloroethylene I I I I I 1,3-Dichloropropane I I I I I 2,2-Dichloropropane I I I I I 1, 1 -Dichloropropylene I I I I '· I Ethylene dibromide (EDS) I I I -!1 1Haxachlorobutadiene I I I I I 11 lsopropylbenzene I I I I I ,1 Ip-lsq~rop:tltoluene I I I I II IMethyl Ethyl Ketone I I I I I ,, I IMethyl lsobutyl Ketone I I I I I 11 Naphthalene I ·1 I I I ii In-Propylbenzene I I I I ii Styrene I I I I I i1, ii I1,2,3-Trichlorobenzene I I I I I ,, ii I1,2,4-Trichlorobenzene I I I I I ;( I• ., I1,2,4-Trimethl'.lbenzene I I I I I I! .. Ii I 1 1 11,3,5-Tnmethylbenzene I I I I I I 1, 1.2-Trichloro-trifluoroethane I · I I I I ii I I, .. ·.> s?M;t~g1a£iMl!ttliiilJi ,11~8~t:1tliXiil~Uf ~;l!&llilltl:~;\jfJ 'i:'~~iE'iil!Ilff§ iii Bromofluorobenzene I 50 I 60-140 I I 65" I I ii 'Ir---------+-I ---+1--1;-----;-I ----'---ii---;-, --.i\ I J~-------~1---~', --;-1--+l--~l--;-l-~\i I a • itc;,crt ;,,,,y Value > MDL: b • l.,stcd Coc,pound, kc Ordcrod b! l.>bct>tO<)' An,h,,::,I Mc<boda: Halo5cna1ed, koc,atic, l!,c:, Rcc,ainins Coepound, ldc~tir,~~ by GC.~,!S. S?;.: COl',C • Spii:ins Conc:cntntion ( <5 x i'QL); AC?~. Acce?t.1blc iungc of PC'e<n<: ~,il.C = ~ Rcc:i,..ryI ~DL • Mc!bod Dc:cc:ion l.,c,it; MB a Mc:bod 81,nt: ND "' Not Dc:e::cd (Below MDL): NA= :Sot Ar.>lyz<d I I I ug/L I ;'it~:::~~==#=~l;~~~= "';;·,. 1 :::::::::•t:;;=:;:::t:::1::;::1:::::::::::::!::::::::1:::::i:;:::;:1:::::111::;1:::!:1:1r::11::i::::!:!:::1:::::11!::::1~1:i:!~l:1:11:i:111:i:1:!:~::11:::1::111:1:111:::i::i11;:=i~1w:~~:;::1::i:11::::i: ~f:-02 1 E.Wti=;J:hfo@f?%i:=ift{f!ttmJ!Ji@\@i:I;i\}JHJ/Ml@i@J@¢.CtgffP:$.A'.MPEE.Jtp1@:J ,w,~,~! I I •i:\fWtcbMP.bONbirh\=:l:Ht::::;r+N•(:ttPt{:trtrnWttt:@:tJl\li#=:ll ftMbBfil fitfMB\Xlf rn:t:::1~::rttilllt:t/:'\i:?•::r::: :•:••:•:•:•::-::'·•·•·••.•:•:::::::<:::•:•. Bromobenzene I I Bromodichloromethane I I Bromoform I I Brom om ethane I I Carbon tetrachloride I I I Chloroethane I I Chloroform · ·· · I I I 1-Chlorohexane I I Chloromethane I I Dibromochloromethane I I Dibromomethane I Dichlorodifluoromethane I 1, 1-Dichloroethane (1, 1-DCA) -I I 1,2-Dichloroethane (1,2-DCA) I 1, 1-Dichloroethylene (1, 1-DCE) I I 11 Itrans-1,2-Dichloroethylene I 11IDichloromethaneI 1,2-Dichloropropane I I I I cis-1,3-Dichloropropylene I I I trans-1,3-Dichloropropylene I ·1 I 1, 1, 1,2-Tetrachloroethane I :\ I 1~~_:_ t:_~c_ 2 h_~o-~ 8 o~-r~-~Y~~~- 0 n_r~-~~t-~-~~ 8 l ______ ~--+----.~---'\'--_--'1\ 11-1-'-, 1__._,_1 -_T=-r..,....ic_h_lo"'-ro_e_,th_a_n_e~(_11_1_-....,..T-:-:Cc--A+)----+I ---+----+--~----'''-----,ii I l1,1,2-Trichloroethane(112-TCA) I. I !I Trichloroethylene (TCE) I I ii 1,2,3-Trichloropropane I I 1! I . ITrichlorofluoromethane I I ii Vinvl chloride I ii1;:::;:=:====================::=====:::==~=====,==,1Benzene ,. 5' ND I Chlorobenzene I !I 1-1....;..,2_-_D_i_ch_l_or_o_b_en_z_e_n_e ________ -+----+----+-----+----+-I ----,!\ I 1,3-Dichlorobenzene I 1, 1,4-Dichlorobenzene I !I 1E-=-t-hy_l_b-en_z_;_e.....:.n.....;,.e ~~-----------+-G-. S'--l-----+--ND--;...---+-1 -----'!\ I IToluene b, 5" ND I i\ I I I ANALYTICAL TEST RESULT (cont'd) I 1 .. · ·,,,~ ,.:· :/.=:x:oMPOUNDYo)t:<tt=ttJt:i':Fttt't\'t::t:t::=:::f/tt/\::1l:::::fM0Dt:@::=:i:rnvtB:\1t r::::===tu:\,ttJ,r#t:::=:<,t:tt: :tt:=::=r:::::Jr:,:::? ii lm,p-Xylenes · I I · I I 'I I I Total Xylenes I ,e,.5' I ND I _ I j Acetone I I I Acrolein I I I Acrylonitrile IIBromochloromethaneI I n~ Butylbenzene I I I. sac-Butylbenzene I I 1;-It_ert_l-c::-:--:B_uty_.__lb-:-e_nz:-e:-n_e-:----:-------,------~-----+-------,---+----...!..1 __ ___;11 11 2:------:C=-:h---:-lo_r_oe:--t-:-hy._lv_i_ny._l_e_th_e_r _______ -+-__ -+-__ -+----+------!l __ ___;II I 2-Chlorotoluene I 11 I4-Chlorotoluene -· I I IDichlorodifluoromethane I ! I cis-1,2-Dichloroethylene I I 1,3-Dichloropropane I I 2,2-Dichloropropane II1, 1 _:_ Dichloropropylene .. I Ethylene dibromide (EDB) I I IHexachlorobutadiene II lsopropylbenzene I Ip-lsopropyltoluene I I I IMethyl Ethyl Ketone I I\ IMethyl lsobutyl Ketone I II Naphthalene ·1 ii I 11-ln--~P~r-o-py~lb~e-n_z_e-ne----------+---~,--_,~--4------__!__---"ij 1!1-S_ty..__r_en_e ___ · ------------+---·-+I __ ___,_ __ ___!.. __ ____.!.. __ ----"ii I1,2,3-Trichlorobenzene I Ii .I 1 l1-'-.2-'.-4-_-=T~ric~h....,..lo_r_o.,-b-en_z_e_n_e---------+-----,l---;-I -,-------+-, ----'-----'I\ 1,... 11--'-,2-',_4_-_T_rim_et_h..L-y_lb_e_nz_e_n_e _______ --+-----:l ___ ;-I ----+-I __ __:I ___ !: I Ii1,3,5-I rimethylbenzene I I I. I I . 1; I 1. 1.2-Trichloro-trifluoroethane I · I I I I Ii I Bromofluorobenzene I 50 I 60-140 I I GS" I I I l 1~~~:~~:--~1--~~1 ---;-:~-\\ I I I I I !I I .. :l.c;,a-t Any Value > MDL= b • Listed Coc,pound, Ace Ordered br uba-><OC}' M•ltial Methods: H•lo5cn .. cd, NOCJ3UC, ~.n Rccainins Coc:pound, ldc~tir,.~ bt GC.-:.(5. 5?i: CO:'iC • Spii:ins Conccnir•lion ( <5 z ?QLJ; AC?~ Acccpuble R>nsc o( Pc:c.<nt: !",RC = ~ Rc<,wc:-y ·.I ~OL" Mc:!>od Dc«c:ion Llc,it; MB= Mc:bod Blank; 1'0 = Not Oc:c=cd (S.Jo.., MDL); NA= Sot Ar.•lyzcd I I I ANALYTICAL TEST RESULT a Reporting Unit (Circle One): ug/kg ug/L I I;~;~:;;:;I:::=;1r~:i,~~= ··~t~ ··;-!' I I ~iii,i:&,Ei£if!£i :;i:,b~:;:,,i I :'\ t),tc6MPb0Nti"f6Wtlt?ftft\lt)'.ll:t:ltt:tf\tttf'({%tlfLittfbBtttlffMB\Itt Htt:tt3.tt:1nn::11.sRUflhlftttt?tt Bromobenzene I I Bromodichloromethane I I I Bromoform I I Bromomethane I I , Carbon tetrachloride I I _ I Chloroethane 1 1 1 1 Chloroform -" · 1 -Chlorohexane I I · I Chloromethane I I Dibromochloromethane I DibromomethaneIDichlorodifluoromethane 1, 1 -Dichloroethane (1, 1-DCA) I 1,2-Dichloroethane (1,2-DCA) 1, 1-Dichloroethylene (1, 1-DCE) Itrans-1,2-Dichloroethylene I Dichloromethane I 1,2-Dichloropropane I I cis-1,3-Dichloropropylene I IItrans-, 1,3-Dichloropropylene I ·1 1, 1, 1,2-Tetrachloroethane I I 1, 1,2,2-Tetrachloroethane I I ··1 Tetrachloroethylene (PCE) I I 1, 1, 1-Trichloroethane (111-TCA) I I I I I\ I 1, 1,2-Trichloroethane (112-TCA) I I I I t-T---'ri_ch_lo_r_o_et_h..._yl1_en_e_(T,.___C_E.,_:) ---------;-I ---+-----+---~I __ --;..I __ ___,ii 1,2,3-Trichloropropane I I I Ii I ITrichlorofluoromethane I I I ii 1:=:V;:::::in=iv=I =ch=lo=r=id=e===========:::====:::=====::===::::;1==='=====1.1 Benzene 6. 2G ND I No I 11 I lf------------~~--t-----+----+-1--,;-----1 Chlorobenzene 1,2-Dichlorobenzene I I i 1,3-Dichlorobenzene I I II 1 1\..-1~,4-.--D-i-ch_l_or_o_b_en_z_e_n_e--------+----+----+---~,'----_~I---!\ Eh I b I I Illt1venzene6. 2.b ND NO1 '\-IT_o ..... lu.._e_n~e~_;_;__------------+----'~;:;......=2...::....~--+----+'--N-IJ>--'l'---'-ND-_._I ---i\ I ANALYTICAL TEST RESULT (cont'd) I I I I I I I 1· 1 · .... :',::-::::::r:coMPOUND':'(b)':'t:'t:/={::}f?'f{ittttfttf:t}t:::ift:J:(::bfMDW:t:f= t}tM'B:\ff: b!J\Q'.$=\:=::\\l==:=:t:::ns=t,rtt:J'f\}}),,:} ii I I I I I m,p-Xylenes Total Xylenes Acetone Acrolein Acrylonitrile Bromochloromethane n -Butylbenzene sac-Butylbenzene Itert-Butylbenzene 2-Chloroethylvinyl ether 2-Chlorotoluene 4-Chlorotoluene IDichlorodifluoromethane cis-1,2-Dichloroethylene 1,3-Dichloropropane 2,2-Dichloropropane 1, 1 -Dichloropropylene Ethylene dibromide {EDS) IHexachlorobutadiene lsopropylbenzene Ip-lsoeropi'.ltoluene IMethyl Ethyl Ketone IMethyl lsobutyl Ketone Naphthalene In-Propylbenzene IStyrene I1,2,3-Trichlorobenzene I1,2,4-Trichlorobenzene I1,2,4-Trimeth]'.lbenzene I I 12. g I I I I I I I I I I . -: . I .. I I I I I I I I I I I I I I I ., I I I I I I I I I I I I IIINDINl> I I I I I I I I I I I I I I I I I I I I I I I I I. I I I 11 I I Ii I I I I I I I I I I I I I I I I I I I I I I •. I T I -I I I I 11 I I I I I I I I I I I\ I I I II I I I ii I I iiIII I I I Ii I I I i! I, I I I 11 ii I 1 111,3,5-Trimethylbenzene I I 1, 1.2-Trichloro-trifluoroethane I · l I . I I ii I Bromofluorobenzene · I So I 60-140 I I '/0+ I 50+ I I I I I I I I I I I I I I I I I I I a • Rc;,cr.AnyValuc > MDL: b • Listed CoopoundsAre 0..dcred byubor>t"')' M:illic:al Methods: H,lo5en,1ed,Arooalio. t!>en Reo•inins Coopound, lde~ur,e~ by GC.'-tS. S?i: CO:-C • Spii:in5Conc.cnirolion ( <S x ?QL); AC?~. Ac:cc?uble Ronge oCPcrc.:nt: ~,-.C = ~ Rcco,..ry I !-!OL a Mc:hod Dctcc::ion Licit: MB a Me:bod Blonk; 1'D = Not Dc:c::ed (Below MDL); NA" 1'ot Ar..:il)"?ed t-Outtide QC limits I ii 1\ 1: ji I I I ANALYTICAL TEST RESULT a Reporting Unit (Circle One): ug~g ug/L I : -:::-:-o:j:\,\:t:trnur,:1r::t:r:r::tww1n;r::;:1:::Jrtr:11rtttt=D.A.J$:1\NADYZE0:n1:::t1 oa -,~-% f:;\(:f\}f:ffii\P?tJ!:t@?t/iJ::}tttttiflt!WfilIMPA~)3Xi'RX¢:rEtntrl NA I ::< itf:)::;}t\:j{'}:t:U:NJ:f)l@tJ}ff@I'iI@If@ilif{ffMlD5ftttrt6tfFACT6Rhf:I' , fti.f'./?}\:{iii::f?}\lt::=ttm:ftt::11::::f}i/:::rnt:::::rtt\tt:tm:iJ:.sXM:etE:'i'.b'f]i/itit BO'l 2 -Otf I ::\'t'f/cbM'PbDNO:YBYt::!It:::::::nwr:::trttfttt@ttittttt:{tt'ttttt lIMbHtff iffj''MBYitl :1ttd- Bromobenzene I . I Bromodichloromethane I 1 ,1-B_r_om_of_o_rm ____________ +----+----+----+-----+-------il, Bromomethane I Carbon tetrachloride I I Chloroethane I Chloroform --· I I 1-Chlorohexane I Chloromethane I Dibromochloromethane I Dibromomethane Dichlorodifluoromethane I 1, 1 -Dichloroethane (1, 1 -DCA} I I 1,2-Dichloroethane (1,2-DCA) I I 1, 1-Dichloroethylene (1, 1-DCE) I . I trans-1,2-Dichloroethylene I iiIDichloromethaneI ! 1,2-Dichloropropane I I i cis-1,3-Dichloropropylene I I I · 1 trans-1,3-Dichloropropylene I ·1 I 1, 1, 1,2-Tetrachloroethane I I I 1, 1,2,2-Tetrachloroethane I I I Tetrachloroethylene (PCE) I I I 1, 1, 1-Trichloroethane (111-TCA) I I I 1 11, 1 ,2-Trichloroethane (112-TCA) I II Trichloroethylene (TCE) I II 1,2,3-Trichloropropane I \i 1 1~T~ri~c-hl-or-o-flu_o_r_om_.__et~h-an-e--------+---+----+-----+---~l---;I\I Vinvl chloride I BenzeneIChlorobenzene 1,2-Dichlorobenzene I 1 ,3-Dichlorobenze·ne 1,4-Dichloro.benzene Ethyl benzeneI !Toluene I 5.3f NO I I I I I ANALYTICAL TEST RESULT (con rd) I I I I I I I I I I I I 1 · ..... ·./·.·····.:::.:=:toMPOUND===(iSyt:·fif:\(=/:::-:f//t:t=:=t.,.=::•t}/:::/\{t:::=::::\:/f:=·<MotY:=-=} ::}{:'MB\:::t::: t,'::::=: '.lJji{:::•:':f:J•::::::::=:?=:··::•,=:?t=:=:f:·::==}•::\:?=:::::,:::> ii lm,p-Xylenes I I I I IITotalXylenesI /6./ I ND I I Acetone I I I I Acrolein I I I Acrylon itrile I I I Bromochloromethane I I I I n-Butylbenzene I I I sac-Butylbenzene I I I I I I Itert-Butylbenzene I I I I 11I. 2-Ch loroethylvinyl ether I I I I ii 2-Chlorotoluene I I I ji I4-Chlorotoluene I . ·.:. I I I I I -.. IDichlorodifluoromethane I I I I I i I cis-1,2-Dichloroethylene I I I I I I 1,3-Dichloropropane I ., I I I 2,2-Dichloropropane I I I I I 1, 1 -Dichloropropylene I I I I .. I Ethylene dibromide (EDS) I I I -11 IHexachlorobutadiene I I I I I ,, lsopropylbenzene I I I I I 11 Ip-lsoerop:tltoluene I I I I II IMethyl Ethyl Ketone I I I I I ii II I\ Methyl lsobutyl Ketone I I I I I I! Naphthalene I ., I I I !I In-Propylbenzene I I I I ii Styrene I I I I I IIi I I1,2,3-Trichlorobenzene I I I I i ., I, i I1,2,4-Trichlorobenzene I I I I I i I1,2,4-Trimeth:tlbenzene I I I I I i i I 1 1 11,3,5-Trimethylbenzene I I I I I I1, 1,2-Trichloro-trifluoroethane I · I I I I :\ 1 r xI00~R~~~&lftff ¥1fttiliii 111~t21;;:: ,'~i1ttt.Jit I;~lt~11ii·it+t&~I I!.%'.'.ti\rnl ·t%RC/ I I Bromofluorobenzene I SO \ 60-140 : \ 6G \ : l! I,~------~,-~,~-+-,--+-,-~,-~,-~,! I I I I I I !i I I • R<?crt Any Vah,< > MDL: b -l..ist<d Coc,poundsA:c Orde-cd br uba-a<oryMaltictl Mc<boch: Haloscna«d,Acoc,aOC, tli•~ R«:iainins Coepound, ldc~ti~ .• ~ by GC.~\S. 5?i-COSC • Spii:in5Conccnrnuon ( <S z ?QL); AC?~ A=?ublc iungc o(Pc:"c:nt: !",RC=~ Rcca,..ryIMOL" !-ic:!>od Dct«:ion Llcit; !-iB a Mc:bod Blonk: ND= Not Oc:c:cd (Below MDL); NA= Not Ar.olyzcd I I I ug/L I '.::\::;:::=::;):t::::i:::;::::::ii:::::t::;:;::;;i;:;:}:;ii::t;::i::::1:!:\1::::i:::::::i:::::1:111:::1:;::::!:: 1 l:i:l:::1::til:l!l!l\:l\l::i:::1:1:;1::::::ll!l::1::i:1111:i:!:~:k~:;~~a:l:::l\\:::'.\::;1; 82i~ ·9 I I I iaESE:iiiiJ!ii! = I t::()\=cbMP.OUNiY:'r6t:t:H:iJM?n::t:tJMJtt@ttJtMttt?t:t:@t:::n::tt :tfMbtfatt tl'fMlllkHPttfai(ltf: Bromobenzene l I I I Bromodichloromethane I Bromoform Bromomethane Carbon tetrachloride I Chloroethane Chloroform . ._•. I 1-Chlorohexane Chloromethane Dibromoch loromethane I I Dibromomethane Dichlorodifluoromethane I I I 1, 1-Dichloroethane (1, 1-DCA) I 1,2-Dichloroethane (1,2-0CA) 1, 1-Dichloroethvlene (1, 1-DCE) I~------'-'---~----+------+----+---~--+---'--' I . I l~------.>-:----L-------+-----+----+-----+-----+---1 I I ltrans-1,2-0ichloroethylene I Dichloromethane 1,2-Dichloropropane I 11 I cis-1,3-Dichloropropylene I trans-1,3-Dichloropropylene I 1, 1, 1,2-Tetrachloroethane 1--_....:....:.....___;:_; ___ __;:_.,!.._..I.-L.----------!...----4-------+----+-------''----' 11------'-------'---'-..L--------+----+----+------+-------,e----l I I 1, 1,2,2-Tetrachloroethane I Tetrachloroethvlene (PCE) I I 1, 1, 1-Trichloroethane (111-TCA) I I 1, 1,2-Trichloroethane (112-TCA) I I Trichloroethylene (TCE) I I 1,2,3-Trichloropropane I I I Trich lorofluoromethane I Vinvl chloride I Benzene G.4 NP I I Chlorobenzene 1,2-Dichlorobenzene Iil~----'----'-----L----------+------'------+------+---,---~li 11 i~~:::::::::::::::==================;==:::;:=====;:====I ====;ii I I\, ,~~.:...:..::_------------+-----=-:......:...._-+---+--...:....:..;.._---+----+-, -~, I I I 1,3-Dichlorobenzene I 1,4-0ichlorobenzene I IEthyl benzene I 6,'1-ND I ! Toluene I G· 'I: NP I I ANALYTICAL TEST RESULT (cont'd) I I I I I I I 1· I·.· .. ··,,::.:+.:::CO MPOUNI5"':(b)'\:=:{?}J(t?'/Wtt=J't:tftb:t(?fi?t{Ff \:fMDt%tfkftMB?t:f: b}:::J'=:gf,',/\k=t:t\tt::ftt':f:::tt'f\H:},=\'' I I I I lm,p-Xylenes Total Xylenes Acetone Acrolein Acrylon itrile Bromochloromethane n-Butylbenzene sec-Butylbenzene Itert-Butylbenzene 2-Ch loroethylvinyl ether 2-Chlorotoluene l4-Chlorotoluene IDichlorodifluoromethane cis-1,2-Dichloroethylene 1,3-Dichloropropane 2,2-Dichloropropane 1, 1 -Dichloropropylene Ethylene dibromide (EDB) IHexachlorobutadiene lsopropylbenzene Ip-lsoeroe:tltoluene IMethyl Ethyl Ketone IMethyl lsobutyl Ketone Naphthalene In-Propylbenzene Styrene 1,2,3-Trichlorobenzene 1,2,4-Trichlorobenzene 1,2,4-Trimeth}'.'.lbenzene I I I ,q. :2. I I I I I I I I I I I I I I I I I I I I .. I I I I I I I I I I I I I I I I I I I I I I I I ., I I I I I I I I I I I 1,3,5-Tnmethylbenzene I 1, 1,2-Trichloro-trifluoroethane · I I I I NO I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I Bromofluorobenzene · I SO I 60-140 I I 65' I I I I I I I I I I a • R<;>ort Any V,luc > MDL: b • listed Coc,pounds Ace Ordc-cd br ubor>l"')' An,ltic:31 ~!«bods: H,lo5cn•«d, Acoc,,tic, tbe:i Rce1,inin5 Cor:pound, lde~~r,c~ by GC.~!.S. CO:-.C • Spiking Conccntntion ( <S :r POL); AC!'~ Accc?t.>ble iunge or Pc::"e.:~,; !.ilC = '° Rceo,..ry . I Y.DL c Me:!>od Dctccion l.ic,it; MB " Mc:bod Blank; 1-D = Not Det..:ed (Below MDL); NA " 1-ot Ar.>lyzed I I 11I, 11 Ii I I I I I I I 11 11 11 II i II Ii ii i II I I! ii i: I• I'. I I ug/L I 1;;~~;~;;~:::~==~=r=~~:~=I Io•~-" I tt}'.,f\/t\::J:Ittt:=tl:tI['t{l{t@ttWit}t:tl!:tft}Illt5ttttfi6N)fAcr6'Rifft , I ,:i:t:::1t:•:1rr::ri1:::::::::::r:::t:r:mi:mrttr:::tt:,Imttt::1trJ:itr:JJt:(1fsXMPtE:,1;n=tt@tttt M/f2. -~ 1 1 I Bromobenzene I I Bromodichloromethane I I Bromoform I I Bromomethane I I Carbon tetrachloride I I -I Chloroethane I I Chloroform -,· · · I I 1 -Chlorohexane I IIChloromethaneII Dibromochloromethane I I Dibromomethane I Dichlorodifluoromethane I I 1, 1 -Dichloroethane (1, 1-DCA) I I · I 1,2-Dichloroethane (1,2-DCA) . I i 1, 1-Dichloroethylene (1, 1-DCE) I 11 Itrans-1,2-Dichloroethylene I I\ I Dichloromethane I ! 1,2-Dichloropropane I I cis-1,3-Dichloropropylene I I · 1 trans-1,3-Dichloropropylene ·1 · I 1, 1, 1,2-Tetrachloroethane I I ··I 1, 1,2,2-Tetrachloroethane I I 1 1Tetrachloroethylene (PCE) I I 1, 1, 1-Trichloroethane (111-TCA) I I \\ 1 11, 1,2-Trichloroethane (112-TCA) I Trichloroethylene (TCE) I ii 11--1-,2-.-3--T-r-ic_h ..... lo-ro_p_r ..... op_..;a;__n ..... e--------+---__,_----+-----+-------;l-----:li I ITrichlorofluoromethane I 1 1VinylchlorideI l~:::::::!::::::==::::::::::::::::::==========~===*===;::====;====*1===,, Benzene 6,81 l'IDIChlorobenzene I I 1,2-Dichlorobenzene I I I 1,3-Dichlorobenzene I II 11,-.:1:..!.., t._:_. -....:D::..:i-=-ch..:.:.lo-=-r--=-o-=-b-=-en..:.:z:.:.e.:..:.n..:.:e --------+---+----+----+----1:--------:\[ IEthyl benzene 6.if I . NP II !Toluene ,.2J I /ID I ii I I I I I I I I I I I I I I ANALYTICAL TEST RESULT (con rd) 1 · ... >:,: .... : /tcoMPo@:r:>:reJ:t::=::::::::::;=:::=:::::r;::::::::::::::rt::::::=:=:::::':t:::::t:.:::r:::::::::?::=t::t.::::rf.'.::;;Mnt:::::t: :::\t'MBt::tt t>:ts.1:::::::-::::r:1,::::::>:::::::c::::::.:::::r::::::::L::::r:.::.::.::::::::,: :: 11 Im,p-Xylenes I I I I IITotalXylenesI :2.0. 4-I ND I I Acetone I I I I Acrolein I I I I Acrylon itrile I I I I Bromochloromethane I I I n -Butylbenzene I I I I Isac-Butylbenzene I I I I I Itert-Butylbenzene I I I I 12-Chloroethylvinyl ether I I I I 2-Chlorotoluene I I I I 1' I4-Chlorotoluene I .. I I I I .. I IDichlorodifluoromethane I I I I cis-1,2-Dichloroethylene I I 1,3-Dichloropropane I I I 2, 2-Dich loropropane I I I I 1, 1-Dichloropropylene I I I •, i Ethylene dibromide (EDS) I I -I IHexachlorobutadiene I I I I ii lsopropylbenzene I I I I I Ip-lsoeropl'.ltoluene I I I I IMethyl Ethyl Ketone I I I I ii IMethyl lsobutyl Ketone I I I I II Naphthalene I ·1 I I I ii in-Propylbenzene I I I 1IStyreneIIIIi I1,2,3~ Trichlorobenzene I I I I I Ii I1,2,4-Trichlorobenzene I I i I i 11 I1,2,4-Trimethl'.lbenzene I i I i I! .. IiI ' I, ,. II 'ii 1,3,5-I rimethylbenzene i i I I . i I 1, 1,2-Trichloro-trifluoroethane I · I I I I ii I, ....... ti,;'.0~fl;(illlliliii til~~2?i1S\1ifir81 t\~Biiiff ;t1t1}1lr:: ~t~itli~Jf:~ijf ;IT Ci! I l Bromofluorobenzene I SO I 60-140 I I 66 I I ij __________ I ___ I ____ I ___ I ---1 __ _;....i __ \\ I I I I I I I I !i I I I I I I · !I I a • R<rcrt Any Value > !,10L: b • Listed Coc,pounds Arc Ordered by ubentory Mahicil M~:hods: Halo5cn•tcd, A<oc,atic, <!>en Rc::uinin5 Coepounds ldcntifie~ by GC.~!S. S?;; C01"C • Spii:in5 Conc.cntntien ( <S x POL): ACP ~ Aec.cp<.>blc iunge of Perun,: !",~C = ~ Rec:,,"')' I ~OL." Mc~ De:cc:ion l.ic,it; MB a Me:bcd Blank: 1-D • Net De:c::ed (Below MDL); NA= Net Ar~lyzod I I I ug/L I :=\'(\t:·cbM'PbUND1't61tt:::::n::\titftt@:Jt:t::tlt:t@t:@:t%Hf%Nftl ltMbBftt ll}MBttI:::=:: l]lMd:if{:::=:::.:::=tt::,:r:::w:::r::::=tfo - Bromobenzene I I Bromodichloromethane I I Bromoform I Bromomethane I Carbon tetrachloride I I Chloroethane I Chloroform · ·· · I , 1 1-Chlorohexane I· I Chloromethane I Dibromochloromethane I Dibromomethane Dichlorodifluoromethane 1, 1-Dichloroethane (1, 1 -DCA) I 1,2-Dichloroethane {1,2-DCA) 1,·1-Dichloroethylene (1, 1-DCE) Itrans-1,2-DichloroethyleneIDichloromethane . 1,2-Dichloropropane cis-1,3-DichloropropyleneItrans-1,3-Dichloropropylene 1, 1, 1,2-Tetrachloroethane I 1, 1,2,2-Tetrachloroethane Tetrachloroethylene {PCE) 1, 1, 1-'-Trichloroethane (111-TCA) 1 11, ! ,2-Trichloroethane (112-TCA) Tr1chloroethylene (TCE) 1,2,3-Trichloropropane I. ITri ch lorofluoromethane Vinvl chloride BenzeneIChlorobenzene 1,2-Dichlorobenzene I 1,3-Dichlorobenzene 1,4-Dichlorobenzene IEthyl benzeneI !Toluene I I I I 5 5 5 ND I ND I ND NP ND ND 1 I I I I I 1 I I I I I I I 1 ANALYTICAL TEST RESULT (cont'd) 1 · ... ),:: :.:'/.=:coMPOUND='(b):=t:f:}'ft}f?'Wfftltt:fft{if)J::{/}/:}b?:MobtfHfHH.JBff:t b.HiMSftt\l=X;\':t(tf/t=rl::&it(i{\i)} ii lm,p-Xylenes I I I I IIITotalXylenesI ,s-ND I ND I I Acetone I I I I Acrolein I I I Acrylonitrile I I I Bromochloromethane· I I I I n -Butylbenzene I I I sac-Butylbenzene I I I I I I Itert-Butylbenzene I I I I ,1 I, 2-Chloroethylvinyl ether I I I I ii 2-Chlorotoluene I I I I I 1iI I4-Chlorotoluene I .. I I I I I IDichlorodifluoromethane I I I I I I cis-1,2-Dichloroethvlene I I I I I I 1,3-Dichloroprooane I I I I I 2,2-Dichloropropane I I I I I 1, 1..:.. Dichloropropylene I I I I '· I Ethylene dibromide (EDB) I I I I -1, IHexachlorobutadiene I I I I I 11 lsopropylbenzene. I I I I I 11 Ip-lsoeropyltoluene I I I I II IMethyl Ethyl Ketone I I I I I Ii I! IMethyl lsobutyl Ketone I I I I I 11 Naphthalene I ·1 I I I ii In-Propylbenzene I I I I ii IStyrene I I I I I I 11 I1,2,3-Trichlorobenzene I I I I I ii I1,2,4-Trichlorobenzene I I I I I i\ 1~11~,2~.~-~-_T=r~im_e_t~h~yl~b_en_z_e_n_e ______ ___c_··-·+l __ ~l---.---+l __ ~l-,-_~!i I ' Ii 1,3,5-t rimethylbenzene I I I I · j! I1, 1.2-Trichloro-trifluoroethane I · I I I :: r:::=:}=:'.:J=:0=r=r=R=:f=.•h=:fj=){=;):;:1:l=:\l:t1t)=i:\l::):::::::f!\i;t==j)\t=t}I;=::!:I\=\'.\:~\:'=.=::lii!l\=.=filt==:J)I::;::I\ ::==1:\:\i\i===:l::il\:c=\{~o=.rt=:~=;:::=::r*::l:={t=r=.,,r=s==r::::::;:1:J=\:i:l=l!r=·:l=·:c=\:\I=::\'.I;;=l(::\=:\r=:sr=:::f=:::::=::ti::;:r ··=t::=~=}1={~:=:~::::,=·< =%=R=,c= .•• = I Bromofluorobenzene I SO I 60-140 I 71 I 6S I ii I I I I I i, I 1:1 =========-=-=--=--=--:-=--=--=-~;-..-I--~----+-;-1-=--=--=--.!....1 l ~~~~~~--:ii I .. rlc;-c:n Any Value > MDL: b -Listed Coc,pound, NC O<dered bt ulic>rat"')' Al'loltial Me:bods: Halosenated, .voc,atic. cbe:, Rec,•inins Coepound, l<!c~tir,.~ bt Gc.~!.S. S?i: CO:'-C • Spi'tins Conccntr>tion ( <S x i'QL); AC?~. Ac:c.cpuble iunge oC Pere:~,: !.i:.C = ~ rlcc.o,-eryI !',1,0L"' l-ic:.bod Dctccion lic,i1; SIB= Method 81,n'<; 1-D., Not Dc:e:ed (Below MDL); NA= 1'01 Ar.olytod I I I I I I I I I I I I I I I I I I I I QNQC REPORT Reporting Unit (Circle One): ~ug/L I. Matrix Spike (MS) Matrix Spike Duplicate (MSD) DATE PERFORMED: 02.-12-C/b BATCH: C/6BOl/-2. LAB SAMPLE 1.0.: BOl/-2 -OJ 1,1-Dichloroethene 27'1-28'/. 103 2.7., IOI 3 60-140 40 Trichloroethene '2.1lf 'Z.f2. 103 2-80 !02 0 60-140 40 Chlorobenzene 2-'lc/-302. 110 302. 110 o 60-140 40 II. Laboratory Quality Control Check Sample DATE PERFORM ED: 02. -12. -q, BATCH: 9GBD'f2 LAB SAMPLE 1.0.: VAL787 '- 1, 1-Dichloroethene JOO. 00 /2.'3.00 }2.3 80-120 Trichloroethene /00. oo . //'I. oo 80-120 Chlorobenzene /00.00 /'2-1.00 /2/ 80-120 80-120 80-120 80-120 80-120 ANALYST: DATE: NOTE: QC limits for LCS/LCSD recoveries: 70-125% I I I I I I I I I I I I I I I QNQC REPORT Reporting Unit (Circle One):Sug/L I. Matrix Spike (MS) Matrix Spike Duplicate (MSD) DATE PERFORMED: BATCH: LAB SAMPLE I.D.: II. Laboratory Quality Control Check Sample DATE PERFORMED: 02-12.-96 BATCH: 9GB0'f2 LAB "SAMPLE I.D.: VAL$"27C ANALYTE><:::==:t:JJSPK:coNCttl?:tRESULT}l@:tt:ltt%':RECOVERYIHt:.:{fAGPJ%}%J:r1 I 1, 1-Dichloroethene /00. 00 /'2.2. 00 I 80-120 Trichloroethene JOO. 00 l'J..lf, 00 I 80-120 Chlorobenzene /00, oo tt'l,00 I 80-120 I 80-120 I 80-120 I 80-120 I 80-120 I ANALYST: NOTE: DATE: CKY Lab QC limits for LCS/LCSD recoveries: 70-125% I I I I I ANALYTICAL TEST RESULT a Reporting Unit (Circle One): ug~g ug/L I ;;:;;::;];;iki~£:::*::r:K~;z:=~= ·~;:::" I • rJtt:tt',,/:Jt:lftttumr:,rt:/Jt=:::1:::::wr1w11rn:::rtttttottttrto'N)=-Xcro1tttt , I i•:::,a:1tt:tlt:ttt:::::,rt::t:t:tttt:11:rtttt:::\tttit1rt@:/IP*B:$AfXP.tE'.:t:n1:r1t:tiII so,a.-o, 1 I I I I I httttco·MPou'Ntrf6t:trrr1irtttr::111:::mr,ttt::t•ttttr@nwr:t:nmtt ttMbtsmt tttfMB\Itl t::t:fpt:trmr:~ - Bromobenzene I Bromodichloromethane I Bromoform 5".'1-, ND I Bromomethane 2'1. 4 ND I I Carbon tetrachloride ~'f'I NI) I Chloroethane ~,.,. 4-ND I Chloroform f?n NI> I I 1-Chlorohexane Chloromethane 2.7.f · ND I Dibromochloromethane ,.tt ND I I Dibromomethane I Dichlorodifluoromethane '2.7. JI. ND I 1, 1-Dichloroethane (1, 1-DCA) 5.'f~ ND I I 1,2-Dichloroethane (1,2-DCA) f.'l'I ND I 1, 1 ~ Dichloroethylene (1, 1-DCE) ~'f'f N/) I I Itrans-1,2-Dichloroethylene 'i.+9 ND I Dichloromethane . '2. 7. 'f-ND I 1,2-Dichloropropane I f 'l'I ND I I cis-1,3-Dichloropropylene I r,. 'f9 NI) I trans-1,3-Dichloropropylene I ·1 1, 1, 1,2-Tetrachloroethane £'1'1 /'II) I I 1, 1,2,2-Tetrachloroethane I ;.,,, ND I Tetrachloroethylene (PCE) I f.'l'f ND I I 1, 1, 1-Trichloroethane (111-TCA) I 5. 'l'I ND I I 1, 1,2-Trichloroethane (112-TCA) f.'I'! ND I I Trichloroethylene (TCE) F.'l'f ND I I 1,2,3-Trichloropropane I I I Trich lorofluoromethane 5.1#-, NI> I I Vinvl chloride '2.'7.4 NO I I I Benzene I I Chlorobenzene 5.+, NP I I 1,2-Dichlorobenzene s:'f, NP I I I 1,3-Dichlorobenzene §.'f-9 ND I I 1,4-Dichlorobenzene f;. 'f-7 ND I I IEth::fl benzene I I I !Toluene I I I I I ii I I I I I I I I I 11 1 11 I I I I I I I I ANALYTICAL TESTRESULT (cont'd) Benz.vlchloride I ! Acetone Acrolein Acrylonitrile I Bromochloromethane I In-Butylbenzene I I sec-Butylbenzene I I I I, · Itert-Butylbenzene I I I 12-Chloroethylvinyl ether I I I ND I2-Chlorotoluene I 5.'1-Cf I I NPI4-Chlorotoluene I I I Dichlorodifluoromethane I I I I cis-1,2-Dichloroethylene I 5".'I-~ I I 1,3-Dichloropropane ~.lf'I I I 2,2-Dichloropropane · I · I I NC> ND I I1, 1 -Dichloropropylene I I Ethylene dibromide (EDS) I £.'f'f I ND IHexachlorobutadiene I I I I Ilsopropylbenzene I I I Ip-lsopropyltoluene I I I I I I I I IIMethylEthylKetoneIII IIIMethyllsobutylKetoneIIII I I I I INaphthalene I ·1 I I ln-Propylbenzene I I I I jl Styrene I I I I 1,2,3-Trichlorobenzene I I I I I I j! 1,2,4-Trichlorobenzene I I I 111,2,4-Trimethylbenzene I I I I I JI 1,3,5-Trimethylbenzene I I I I i Bromofluorobenzene · I ~ I 60-140 I I IOI I I I I I I I l I I I I IIiIIIII I a • Rc;,«1 A,y Value > !lo!OL; b • U11cd Coc:tpound, Arc Ordc:-cd by ubon<cry A,:,itic:i! Mclbods: H1lo5cn>1cd, Aroc:t><ic. t!lcn Rcc:t>inins Coc:pounds l~cntificd by C-C.~!S. S?:, CO/;C • Spii:ingConccntt,tion( <S x POL); AC? r. Accc?ublc lunge ol Pc:-ccnc; !'" • .:.c = ~ Rcc.o,,:ry I. I L • Mc:.'lod Dctcc·jon Uc:tit; MB = Mctboc! Slonk; :,.;o = Not Octc:::cd (Below MDL); /;A = 1'0< An>I)~~ 11 11 I I I I I I I 11 1! I 11 11 II ,, 11 11 ,. 11 Ii i ,I I 1 I ,, I ll ; i I I ii i! ANALYrlCAL TEST RESULT a Reporting Unit (Circle One): ug~g ug/L li~;;;~t~~if:l:!~~1fiii~=~=I I 02:-" \ J I ~:~:~:::'.:::~;;,i:;:;~:'l::::::;;;:;::;::l:\l:::1;:I:::'.l'.\l::;:::l'.:i:i~!'.!:~::;!l!!:ll;~ll!!:~::'.!!:!l\l\!\llll~::\l:~i;\:!lt:!:l:~:::jl\l!'.\;!'.!~5::::~!l!:!!::\!\!!l!:!:::\l:!~?§:~Ji=~~::l:!:::::l\!::l: Bc,~-02 I ~ fJ'.:(,{;;::/t{t/({@:=t}ttttI:Ittifff]J@::ifWitttttittti/¢'.t:lE.ITT:·$.AM.PLE.':tf;):Hl!: SWBS&SlO~PiS.>I I I. ?W::'.f}c6MP00NDY6Wt}fN/fiti{tltt\tltlttttHfaltJ::i?t:@t :@lMbBtt@llfMB\ttJ :,ttt:f#.iltir-- Bromobenzene · I I I I I I I I I I I I I I I I I I Bromodichloromethane . I I I Bromoform ,.s-ND I I Sromomethane 32.5 ND I I Carbon tetrachloride ,.5" ND I I Chloroethane 32.~. HO I I Chloroform ,:;-· ND I I 1-Chlorohexane I I Chloromethane ;:2. 5" NC> I I Dibromochloromethane ,. ;-ND I I Dibromomethane I I Dichlorodifluoromethane !2S ND I I 1, 1 -Dichloroethane (1, 1-DCA) ,. 5" ND I 1,2-Dichloroethane {1,2-DCA) I b.~ ND I I 1, 1-Dichloroethylene (1, 1-DCE) I ,.s-ND I I Itrans-1,2-Dichloroethylene · I 6.5' I ND I I IDichloromethane . I 32 . .5" I I NP I I ii --'------+-----'--~---'-----------1·1 1,2-Dichloropropane I 6.~ I I NP I I cis-1,3-Dichloropropylene I ~.5" I I N/) I I ij I' ·~ 'I il-----'------'--..-L..---------......::;._--...--_.._--___.---'------11 1trans-1,3-Dichloropropylene I I I I 1, 1, 1,2-Tetrachloroethane I 6.~ I I ND I I ii1;----------'--'_.__--------:-----;------,-----,---,-------,i ii 1 ,. j 1, 1,2,2-Tetrachloroethane I G'.S I I ND I I ITetrachloroethylene (PCE) I I I I I -'---'-___ c_-------------+--~'----'-----;--____;;;--;----;----,.~ ND I1.1, 1-Trichloroethane (111-TCA) I ,s I I ND I I I1.1,2-Trichloroethane (112-TCA) I ,.5 I I NI) I I Trichloroethylene (TCE) I ~., I I ND I I I1.2,3-Trichloropropane I I I I I i: ITrichlorofluoromethane I ,.s I I NP I I IVinvl chloride I 32.S-I I ND I I i-------:------'----,:: I! ~---------------+-___;;_:__........:....-----+-------:-----;----,!I ,, Benzene I I I I I IChlorobenzene I ,.5 I I ND I I j 1,2-Dichlorobenzene I ,.5 I I ND I I ii -----,.-----------+-----+-----+----~---+---~I\ ii I1,3-Dichlorobenzene I ,., I I NC> I I I 1.4-Dichlorobenzene I ,.5 I I ND I I IEthyl benzene I l I I I Toluene I I I I I ---------------+------;.----;---+----:---:----., j( I I ANALYTICAL TEST RESULT (cont'd) t·.:··.'':-:(::··.·::_::::co MPOUNtt(b)::=\t';:::::::/·:::-'::::::::::;::::?:::::::::::,::·}::•:::::: ;:;::;,'?J>\::::}:::?t·::/NfI)Ii'''''':::'''V::-::::::MB }:=:=::t[:~::::::»Jt·:=:::'=-::•:::1:.:•·:•:::::::.;::·,:'\:':0::":?:·::~;::: ?'''?:''. :::: ·'.'-ii - I m,p-Xylenes I I 11 Beriiylchloride ,.5 I ND I II I ! Acetone I I I IAcrolein I I I Acrylonitrile I I I I Bromochloromethane I I I In -Butylbenzene I I I sec-Butylbenzene I I I I Itert-Butylbenzene I I ii 1 12-Chloroethylvinyl ether I I II 12-Chlorotoluene 6.5' I ND I J! I I Chi I I I4-orotoluene .. ! I IOichlorodifluoromethane I I I I I ii cis-1,2-Dichloroethylene I 6~':i I I ND I 11 1,3-Oichloropropane I G.S-I I ND I II 2,2-0ichloropropane I . I I I I 11 1, 1 -Dichloropropylene I I I I 11 Ethylene dibromide (EDS) I G.S' I I ND I I .. 11 I I I IHexachlorobutadiene I I I I I -ii Ilsoeroex:lbenzene I I I Ip-lsoeroex:itoluene I I I IMethyl Ethyl Ketone I I I IMethx:I lsobutyl Ketone I I I INaphthalene I ·1 I In-Propylbenzene I I I I I I I I I I I I I I I Ii I' . : 1 ii q i i i i i I i 1 I 1 I IStyrene I I ;i 1~1~,2~,3--~T=r~ic-h-lo-ro~_b_e_n_z_e-ne~~~~~~~~+-~----'-~l~~----;~~~+--~~~l~~~-i, · ji 1,2,4-Trichlorobenzene I I 1 11,2,4-Trimethx:lbenzene I I j 1,3,5-Trimethylbenzene I II !I 1. 1,2-Trichloro-trifluoroethane · I I jl p,;;:Jh1~{Q;W,~ilf 'Jl':l(;f@iifi,l1l!ll.thfi?J~ :'1 ".01:~~1:mitJc''fOiti'R\0\j;j,', · ttD , I t: I ,i Bromofluorobenzene · I ~ I 60-140 I I 108 I 1! I I I I I I I I IIIIII I • • ~ c;,crt Any Val1>< > MDL: b • Llstcd Coc,pcunds Arc Ordc:-cd by l..lbcraicry An:lhic:,I Mclhods: H,lo5cnaicd, Aroc,•ti;,, then Rcc,,inins Coc:;,ounds !dc~tir,cd by C-C.~!S. S?i: CONC • SpikingConc.cnrr•tion( <S x POL): AC?~ Ac.cc?ub!c ~ngc or Pc:-cc:u: r.;;.c a~ Rcca,-cry I. I L a Mc~'>od Dctc<"Jon Llc,it; MB" Mctboc! Bl:nk: ND= Not Dcte::cd (Below MDL):~.-\= :Sot An>lrzcd I I ug/L I : .:::-:rt::r:',:AJ:r:::: ::s:r::t@tt:t::ttt:trt1:tttrt+rttit1:>'A:1$.ANALYzEo?Jttt 01-12. -ere ii:i:'}/=:HtJ:)::::J)}::;,qJf?lUltll'W:titt:}{/Hf\'ttt]:::o.A'tE::1~x,11tKct Et>:flfi N1' I I I '.~/;~]~~~~~~~~~iii =~,I I :····_-_-: __ · toMPOUNDdbt:··:·.:··:::-:::,., .. ::--·:-:::·::::···:<5>:··:···:····:,.-::,··<:··:,:········,Mou=···,.::,;,::::·:M:s::·-··.·.:: ... : .. :::::··03<-:,-_:::- Bromobenzene I I Bromodichloromethane I I Bromoform 6.2b ND I I Bromomethane 3,. 3 ND I I Carbon tetrachloride 6.2G ND I IIChloroethane31.'3 Nt> I I Chloroform b:ib ND I I 1 -Chlorohexane 1 IIChloromethane3\. 3 ND I I Dibromochloromethane ~.2t IND Dibromomethane IIDichlorodifluoromethane · I 3\.-; INC 1, 1-Dichloroethane (1, 1-DCA) ,.2.G ND Nb NDI1,2-Dichloroethane (1,2~DCA) . ~.2t; 1, 1 -Dichloroethylene (1, 1-DCE) b. 2.~ ND ND ND ltrans-1,2-Dichloroethylene ,.2., I II I Dichloromethane ~l. 3 1,2-Dichloropropane I ,.2' ND I NP n . ..::c:.:.:is:_-_1:..!.:,3::..-_:D::...:i=ch~l=or~o1:.p.:...:ro:r:>P:..L.:..::.Yle.:....:.n.::-..e ------+I ~'.!.:· '2.!==t~----+-----!~--+-----ll ___ lItrans-1,3-Dichloropropylene I ·1 1, 1, 1,2-Tetrachloroethane I G.2' I I ND I NP I 1, 1,2,2-Tetrachloroethane I ,.2., I ·I Tetrachloroethvlene (PCE) I C:.2'> 1,1,1-Trichloroethane(111-TCA) I G.i, NI> I ND I I ND IIl1,1,2-Trichloroethane(112-TCA) ~.zc I II Trichloroethvlene (TCE) b.2'; I ii I I I ND I 1!...1:.!.:,2=.!.,.=..3-_T..:..:r~ic:.:..:h~lo:..:...ro=rp~r.=.Jopc..:a=-n.:.::e _______ --+----+----+-----,---1:--_-----ill·\i I ITrichlorofluoromethane c;. 2.<: I ND Il!::V~in~1v!::!::I ~ch~l~or~id~e~============*=~~'~· 3~*====*=:::::::::::::===:::::p:====i=I ==~II Benzene 1 ~ I ND I ND I I Chlorobenzene c.. ~~ 1,2-Dichlorobenzene r u; ND I Nl) I I I 1,3-Dichlorobenzene ~.1' I II1,4-Dichlorobenzene ,. ~ I !I I Ethyl benzene . I ii 1~1T~o~lu~e~n~e:.:.=::::.:.:::~-----------!-----+-----l--'---~f---T,--,i\ I I I ANALYTICAL TEST RESULT (cont'd) I 1·;,;:b=~;~~:~tlNrt(llf'~'Y:<•''""~ ?'''C''.''<':"\Ct'''.;f (Mt>tF"J''.'MB:;:'T~::-'.l'''(t;:,:·.·-·r ,.·.•.•>><> :l Benivlchloride ,.2.c; I ND I ii I !Acetone . I I I ii Acrolein · I I I II Acrylonitrile I I I !I I Bromochloromethane I I I I ii In-Butylbenzene I I I I :1 sec-Butylbenzene I I IIItert-Butylbenzene I I I I l'-2_-_C_h"C""lo_ro_e_th--=y_lv_in_.y_l _et_h_er _______ ---t-1 ---=--t-1 ---t-1 ---+---~I __ ___;\[ 12-Chlorotoluene I ~.2G I I ND I dIir~-.--C~h-lo_r_o_to-lu_e_n_e----------~,----+,----+1---.-----~I--~!, Dichlorodifluoromethane I I I I !! I cis-1,2-Dichloroethylene I G.1'. I I NJ> I 1! 1,3-Dichloropropane ,. 2~ I N.D I IIIJ--!--=:-:-:-:---L----'-----------+---=---+----+-____;_;-=---+----+------.! I 2,2-Dichloropropane I · I I I I Ii I 1~l1-'-.1---D~i,--ch...,..,l-or-0~1p-ro~p--:-yle_n_e---------+-----:-l---+l----+l------;l--~I! 1i-E_t_hv._le...,..,n....,..e_d_ib.,..-r_o_m...,..,id...,..,e_(..._E_D_B..._____) ______ -:-l _f._. ~-'""7'1 __ --+I_N.D_--+l __ ___,l,___~!i l~H_e_xa_c_h_lo_ro_b~~-ta_d,--ie_n_e _________ -t-l __ -+-l __ --+-l __ --+l __ _!.l __ ~:IIIlsopropylbenzeneIIIII :i I p-lsopropyltoluene I I I I I Methyl Ethyl Ketone I I I IIIMethyllsobutylKetoneIIII INaphthalene I ·1 I I I In-Propylbenzene I I I I 11 Styrene I I I I 1,2,3-Trichlorobenzene I I I I 111,2,4-Trichlorobenzene I I I I 1 ___ , 2-'-, 4_-_T_r_im_e_t_hys....l_b_en_z_e_n_e _______ .. _I -----;-I ______ ~I ----'-I __ _ 111,3,5-Trimethylbenzene I I I I I I I I I I I I I I I I · a • Rc;,crt Any Value > MDL: b • Usted Cccipounds Ace Ordc:-ed by ubcratcxy An>lticil Methods: Halc5cnatcd, Acccistic, then Rce1sinin5 Ccmpound, ldcnur..~ ~y CC. ~!.S. S?i: CONC • Spi<ingCcnc..:nttstion ( <S x POL); AC?~ Accc?ublc !ungc cf Pc:-ccnc; r.;;.c = ~ Rccc,....y I I l-!~L" Mc~'>od Dc1ce"jcn Umit; MS= Mc:bod Slonk; ND= Net Octc:!cd (Belew MDL); NA= Nee ~1)-.e<! I I I ug/l f:).::~:\(:}{:\:::::/:{'./:/t::::tt::;:[::=:::::::l?t:t<:t::::t't:::rt\::r::t\::::::::::rsxa::s'AMPLE:'i'.b'.::tt\:tl'tl Bo'l-2.-0¥-I I I Bromobenzene I I · I Bromodichloromethane I IIBromoform §. 35" NP I Sromomethane 26.9 ND I I Carbon tetrachloride S'JS' NP I Chloroethane 2.,. \?.. ND I II Chloroform 5'..~ l'-lt> I I I. 1 -Chlorohexane I i Chloromethane 2'.2 ND I I Dibromochloromethane f.35" No· I i I Dibromomethane i Dichlorodifluoromethahe ~.i ND I 1, 1 -Oichloroethane (1, 1-DCA) 1 1,2-Dichloroethane (1,2-DCA) 1, i -Dichlor·oethylene (1, 1-DCE) 11 trans-1,2-0ichloroethylene IDichloromethane . 1,2-0ichloropropane I cis-1,3-Dichloropropylene trans-1,3-Dichloropropylene 1, 1, 1,2-Tetrachloroethane I I1, 1,2,2-Tetrachloroethane ITetrnchloroethylene (PCE) I1.1, 1-Trichloroethane (111-TCA) I 11,1,2-Trichloroethane (112-TCA) Trichloroethylene (TCE) I 1.2,3-TrichloropropaneI !Trichlorofluoromethane Vinvl chloride · I Benzene Chlorobenzene I1.2-Dichlorobenzene 1 11,3-Dichlorobenzene I1.4-Dichlorobenzene IEthyl benzeneI !Toluene I I i I I i I I I I I I I I I i I I I I I I I I i:;.35 G".~, 5.~~ 1-,.i I S.3S I 35" I I f.35" I I s-:~5' I I 53~ I I 35" I i 3, I I 3S' i i I I S.3~ I I 2c;, CZ I I I I S.35 I I f3£ I I 5:3, I I S":s, i I I I I I ND I -I N[> i ii NO i ii ND i I ii NP i I !i Nb I I iiI, NI> I I ii I ·1 !I ND I I ii NO I I ii Ii ND i I ii NP i I :i NP I I I! i[ ND I I \i ,: I I ,, ii i I " ND II N!> I I !I I I 1i ND I I !I ND I I :i ,, ND I I ii 11 ND I I j[ I I !; I I I\ I I ANALYTICAL TEST RESULT (cont'd) I Acrolein I I 1 1 1 Acrylonitrile I · I I Bromochloromethane I I I In-Butylbenzene I I ! Isec-Butylbenzene I I I I , I 1 1i II, I Itert-Butylbenzene I I I2-Chloroethylvinyl ether I I I cis-1,2-Dichloroethvlene 5.-S, I NP I 1,3-Dichloropropane 5. 15"" I ND I 2,2-Dichloropropane · I I i i! ii ii II Ii 12-Chlorotoluene 5-35' I ND I I 4-Chlorotoluene I I Dichlorodifluoromethane I I I! 1i , I ii I1, 1 -Dichloropropylene I IIEthylenedibromide (EDS) I 5". 3> I NI> I I IHexachlorobutadiene I I I I I Ilsopropylbenzene I I I I I jp-lsopropyltoluene I I I I I I Methyl Ethyl Ketone I I I I IIIMethyllsobutylKetoneIIIII INaphthalene I ·1 I I I i\ In-Propylbenzene I I I I I '! I :,~,s-~-re~ne__._ ______ ~--~,~-~,--~,--.,--~,-~:i I 1,2,3-Trichlorobenzene I I I I I Ii 1,2,4-Trichlorobenzene I I I I I 11,2,4-Trimethylbenzene . . I I I I I li 1,3,5-Trimethylbenzene I I I I II111.1.2-Trichloro-trifluoroethane I · I I I I ji ... · ·:,:,iD~i~¥tl8:?11~J!i:'.:!l"~f1i+ilr1il1im12 ... ·· • ~E!ietllil!i~?t\Il l:1~ii'c ;;0.00 ,I< w:c I i Bromofluorobenzene -I sn I 60-140 I I IOJ/. I I 1! I I I I I I I I I I I I I I I I I I , • ; te;,«t Any Value > MDL: b • Listed Coe>pound, Arc Ordc<cd by l..lb«ot«y Anoltic,1 Mel.bods: Haloscn>«d, Aroo,ti<, :bcn Rcoainins Coc:pound, l~cntificd ~y CC.-:-.!£. S?:._ COSC a Spii:ingConccncr,tion( <S x POL): AC?~. Accc?ublc ~ng~ o(Pc:cen1: ~ ... c = ;. Rcc:.-:,,-ery I I lo!!:'!. a Mc:.'lod Dc«ction l.ic,it; MS = Mctboc:! Blonk: 1-D a Not Dc«:::cd (B<low MDL): SA= l'-ot Allolyz«! I I ug/L I ;~":l;'.'.~~~~!:;2:;;;;;;';~i~=~~I Io•~!,'% I DILUUONFACTOR-· .. ·:::_:·:· I t.:;.'.:::;::/:~:f:;~::::;,:'.;tt::{::::~tttr:;·;:;;:;::iWtl:tt::,::tt::S::;:;~:::;·:::::;::::::::J;:::t·:;{t',/:t¢.t!IEfili:$'.Afy{PtE.':t:fi~'I:·::::· JWB5&'fJ2Dt. '1 · 1 :··T·<:.-coMi>'bDNt:>tf&t\f?\\-)::/.//:::::::~·:.::::=::.::::::\'.;J:_:_)./.)\:::.:::::::::::.:.:.x:::::::::::::::::-:: i'(MbiJ:L:V .::::::::::::MB;:=::::::::::: :.:.:-:::-.::.:,1.:.::::::::::t': Bromobenzene I Bromodichloromethane I IIBromoformI ,. 'l NO Bromomethane 3 2. tiD Carbon tetrachloride 6.4-NI> Chloroethane I 32.. .ND Chloroform I ~if' ND 1-Chlorohexane I Chloromethane I 32. NI> Dibromochloromethane I f,.f NJ) I Dibromomethane I Dichlorodifluoromethane I 32. ND I b·"' f ND I ND I ND I 1, 1-Dichloroethane (1, 1-DCA) I 11,2-Dichloroethane {1,2-DCA) I 1, 1-Dichlornethvlene (1, 1-DCE) I b,'/- 32. I tf I ND I ND I ND I 11 trans-1,2-Dichloroethylene I Dichloromethane . I 1,2-Dichloropropane I I NP I I II cis-1,3-Dichloropropylene I trans-1,3-Dichloropropylene I 1, 1, 1,2-Tetrachloroethane I ,. 'f. I I ND I ,.,,.. I I I ND I I ND I111, 1,2,2-Tetrachloroethane I ITetiachloroethylene (PCE) I 6.1/-I ,.,,. I f: I I ND I I ND I I ND I I1.1, 1-Trichloroethane (111-TCA) I 111.1,2-Trichloroethane (112-TCA) I ITrichloroethylene (TCE) I I 6-'1-I 32. I I I I ND I I ND I I1.2,3-Trichloropropane II !Trichlorofluoromethane I · IVinvl chloride I I I I I I ND II Benzene · I Chlorobenzene I I1,2-Dichlorobenzene I ,.'f: I I ND I I lf I I ND I I ND I111,3-Dichlorobenzene I I1.4-Dichlorobenzene I I I I I I I IEthyl benzene II !Toluene I I I I I I I I I I I I I I I I I ! I II I I .· I I . I I I I I I I l I I I I\ I II I I\ I !I I II, I i\ 1 i\ I II I I\ I :I I I I I " i; I, l II Ii I ii ,, I · I 11 I \i .1 I l\ I :i Ii I ;, ,, I I I I I I I I ANALYTICAL TEST RESULT (cont'd) COMPOUNr:L(b)\:·/>.:=:::.:.·:::::::':··.~.=·:·=t.· ... :;::;:::,:·:.: .. ::::,::: ... :,:-·:·.:t:=:MDL").:•v: .. ·_MB:·.-;,:.·.::-r.::: .. : .• :::=r:l:(.···.·.·:.:·:.·:··.:·:=rk·.·::: .. :=::>,:.:::il jm,p-Xylenes I I I I I 'I I Beniylchloride I 6,'f. I I ND I I I IAcetone I I I Acrolein I I I Acrylonitrile I I Bromochloromethane I I In-Butylbenzene I I 1sec-Butylbenzene I I Itert-Butylbenzene I !I I2-Chloroethylvinyl ether I ii 12-Chlorotoluene b.4 N.D I I! I I4-Chlorotoluene I · ll IDichlorodifluoromethane I Ii I cis-1,2-Dichloroethylene 6:'I-ND 11 1,3-Dichloropropane 6. t/-ND II j 2,2-Dichloropropane 11! · I I1. 1 -Dichloropropylene II Ethylene dibromide (EDS) I 6.4 I ND I ! IHexachlorobutadiene I I I I II I Ilsopropylbenzene I I I I ii IP"""'" lsopropyltoluene I I I I !i IMethyl Ethyl Ketone I I I I I i! I 1 Methyl lsobutyl Ketone I I I I I I\ INaphthalene I ·1 I I I i\ I 11 n-Propylbenzene I I I I I ii 11 Styrene I I I I I i\ I1,2,3-Trichlorobenzene. I I I I I i\ jl 1,2,4-Trichlorobenzene I I I I I tj · ii 1,2,4-Trimethylbenzene I I I I I i 1 ,3,5-Trimethylbenzene I I I I IIIi1, 1,2-Trichloro-trifluoroethane I · I I I I I Ii Bromofluorobe~z-~~e · ... . I . 50 I ~0~140 I I H~ I I 1! I I I I I I I !~---------+---+-' -----:-' -----+'--+--' --+-' ----:iiIIIII !! I a • Rt;>ort ;..,.y Value > ~OL: b • Llsicd Coc,pounds Ate 0.-dC"cd by ubormry Anoltico! Melhod,: Halosen><ed, Atoc,.tic:, tben Rec,ainins Coc:pound, Identified ~y c.,:.-:,.(5. S?); CONC • SpikingConccn<r>tion ( <5 x POL); AC!'~ Accc,t>blc lunge of Pc-cent: ~i:.C ~ ~ Reco,,::y I I Mctboc! Bl>nk: NO = Not Octc:::cd (Below MDL): NA = Not ;..,.,iyzcd I I ANALYTICAL TEST RESULT a Reporting Unit (Circle One): ug~g ug/L I '.::::::;:::;:'.:::;:::t:::;:r:;:!::::::;:::;::::j!::::i:::,::::::;:::::'.::::1::l:!:::::1;::::::::::1::::l:!:!:\!::):;:::::::ll:::::;:::::!l:l::;!!ll:::::::;:1:;i::;:!:!l!l::!::1111:!lil!:ti~~:~=~a:!:\:!:! 1 0 i:::,/tii:iiiiifr':,:i:ii?iiiiiiiiiiiif{nttutto'N;PAcr61fifi , 1 Bromodichloromethane I I Bromoform ,.21 NI> I I Sromomethane s4.t ND I I I Carbon tetrachloride <,.g/ ND I I IIChloroethq.ne 3'f.l .NO I I · I Chloroform ,.~r ND I I I 1-Chlorohexane I IIChloromethane3'f, l ND I I I Dibromochloromethane ,.11 ND I I DibromomethaneIDichlorodifluoromethane 1.:....:.,_1-__ Di:....:..c:....:..hl--or;...:.o_e __ th:....:..a:....:..ne..:........l...(1~,1 __ -_D_C.::...:A-.:i\)'---~~~~...!....-....x.:..::..:.___..;._.~~--!--~~-4--~~ I 1,2-Dichloroethane (1 ,2-DCA) 1, 1-Dichloroethvlene (1, 1-DCE) 34-.1 ND I I lt '~ I c.it ND I ,.,, NI) I ll Nt> Iltrans-1,2-Dichloroethylene ii I Dichloromethane 1,2-Dichloropropane cis-1,3-DichloropropyleneItrans-1,3-Dichloropropylene 1, 1, 1,2-Tetrachloroethane 1, 1,2,2-Tetrachloroethane ·-1 Tetrachloroethvlene (PCE) 1, 1, 1-Trichloroethane (111-TCA) 1 11, 1,2-Trichloroethane (112-TCA) Trichloroethylene (TCE) 1,2,3-Trichloropropane I ITrichlorofluoromethane Vinvl chloride I I I I I I I I I I 34-. I ii 81 · i, b.~I 81 21 c..gf ,.~, G.il 4.1 NI) I Nl> I ND I 1 NP I I NI) I I II I ND I I 12... I I I ,.,,.0 I I I I I I! I ND I I NI:> I \\ I Chlorobenzene 1,2-Dichlorobenzene IBenzene I\ ii NO I C.21 e,.o I 1,3-Dichlorobenzene IC.il NP II ,L1:.!..,.t..:..· -_:D::.:i=ch:.:.:l=or:..::o=b=en:..::z:.::e::.:n.=..e ________ -+-~::.!....-~---+-~--'---,----+----!\ ,.if 12. I I I 11!-: E=.:t:..:.hYt.:..l-=b=en:..::z:.::e::.:n.=..e __________ ~-----4-------+---,-----+------:1 1IlhlT~o;;,,;;lu~e~n~e===============:!:====::!:==:=::!:===k======='..! I I I ANALYTICAL TEST RESULT (cont'd) COMPOUNtt'ct,);::,::·/:_/0 -,/.:t:f:f:·-,::'''. ·,:·· ... ··.··:····:·· .. :··-.-t:::M:bt····:'"l·:.:::·:MB .. ··:····t:::'":::·:J)l:\-::·_,l.::::_·:·_·_._':_\_····_-_\Jt:::·:_.-:=.-'.···_ /.•:-11 I m,p-Xylenes I I I 'I Benz.ylchloride ,.81 ND I I Acetone I I Acrolein I I Acrylonitrile I I I Bromochloromethane I I In-ButylbenZene I I sec-Butylbenzene I I I Itert-Butylbenzene I ii I2-Chloroethylvinyl ether I Ii 1'-12---C--h-,-lo_r_o_to-lu.,_e_n_e_.__ _________ -t--__ ~-:-. i=-, --+-----+--N-D----;,----.:.....1 __ ___,I! I 4-Chlorotoluene I !I Dichlorodifluoromethane I !i I cis-1,2-Dichloroethylene 6: ii Nl:> I II 11_1...:..,3_-_D_ic_hl_o_ro_._ip_ro ...... p......:a_n_e ________ --+----=6:..;_. 'l-'-'1-+----+-N......:D:..........~--__..!....I --~II 11--2...:..,2_--:-D=i-:-ch-:-l_or_o.,_p_ro_,_p_a-=-ne ________ --+----+----+----+l __ --+l __ ---:l 1 11 I 1, 1 - Dichloropropylene I Ethylene dibromide (EDS) ,.~I I ND I I 1! IHexachlorobutadiene I I I iiI1;-ll-so_p_r_op_y_lb_e_n_ze_n_e-----------+---+---+l----+l------'-1------'li l..,__P_-_ls_o....,_p_ro...,_p...,_y_lto_lu_e_n_e _________ +----+-----+-1 -----+-1 __ __,_I __ ~!i 1;-IM_e_th__.y'-:-I _Et_h.,__yl_K_e.,....to,--n_e ________ -+--__ -t----+-1 ----+-I ----;'----'i! I IMethyl lsobutyl Ketone I I I i\ Naphthalene I I I iJ ' 1~ n----'-P-r-op-y-lb_e_n_z_e-ne-----------i-----+----+1---~--....,_I __ __;;! I ,.,~S-~-re-n~e_,_ ________ -'--_ ____,~-=-~----,--........... --~,-~;1 I1,2,3-Trichlorobenzene I I !! j! 1,2,4-Trichlorobenzene I I 111,2,4-Trimethylbenzene I I 11,3,5-Trimethylbenzene I I I II111. 1,2-Trichloro-trifluoroethane I · I I I I i Bromofluorobenzene · · I SO I 60-140 I I . IIGJ I I I I I I I I I I I I I I I I I I I I I l • ~<?OC'I lvly Value > MDL; b • Listed COClfiOUMds Ace Ordered by ubo.-.1cry Anoitic::,I Melhods: Halosen••cd, Acoc•tic:. then Rec,•inins COC:fiOUMds lden~Ged by c<:.-:.~. S?ii. C01'C • SpicingConc.:nrrotion ( <5 x POL); AC!' r. Ac:.c.c:,ublc lunge or Pc-«n1: !",itC = r. R«:.:,,-.ry I I lo!~!.. a Me:.'lod De:cc•.ion Lir:1it: MS = Me:llod Slonk: NO = Not Octe::cd (Below MDL): NA = 1'01 Molyz«! I I ANALYTICAL TEST RESULT a Reporting Unit (Circle One): ug~g ug/L I l~\~t,:;::~r~~i::i~JK~:~~= 01::·,C • t~~~eE=te:=~=~~B I I i:''::\::'.tt·coMPb0Nti1'iihftHl?ff?NI}=:tn::J::,::::ttt:J:=f::ftf\@tt:t:t:ttJ:::t':: ltMbD:mtm i::l}:MBU(\:j--- Bromobenzene I I Bromodichloromethane I I. Bromoform . 5 ND I I Brom omethane 25 ND I ! Carbon tetrachloride 5' ND I ! I Chloroethane . ZS-ND I I Chloroform >. "lb I I 1-Chlorohexane I IIChloromethaneU-NP I I Oibromochloromethane 5" IND Z.!i ND DibromomethaneIOichlorodifluoromethane 5 5' 5" ND ND ND 11_1....;..,_1 -_Oi_c_hl_or_o_e_th_a_ne___,_(1-'-, 1_-_D_C_A.....,,)'-----------:;....--+-----+------'------- 1 1,2-0ichloroethane (1,2-DCA) I 1, 1-0ichloroethylene (1, 1-DCE) I 5"' 25" 5' ND ND ND ltrans-1,2-Oichloroethylene I I 1:..........----''----------'-------''-----------+--.:;..._-+-----'-=-------+----.....:..----:.--- 1 Dichloromethane I 1,2-Dichloropropane I 5' 5 I ND tit> cis-1,3-0ichloropropylene ·· 1 trans-1,3-0ichloropropylene ·1 1, 1, 1,2-Tetrachloroethane I I 5 I I ~ I I ,, I ND ND ND 1 1, 1,2,2-Tetrachloroethane 1 1 Tetrachloroethylene (PCE) 1, 1, 1-Trichloroethane (111-TCA) I I 5 I I S' I I I I 5 . I I 2.~ I ND I N1> I I ND I ND I I 1,1,2-Trichloroethane(112-TCA) I !I Trichloroethvlene (TCE) I ii ''- 1:....:.., 2:...:..,:....:..3-...;:.T:...:r:...:..ic.:;...h:..Llo:...:..ro.:...:.p.:....r..l..:op:...:a=-=n:L.e--------...;...--==-----!...__;_=---;..-------!.-----'l-----:li I ITrichlorofluoromethane I ii Vinvl chloride I I\ BenzeneIChlorobenzene 1,2-0ichlorobenzene I I I l~:!::::::=================;::==:!!!====::;=:::::::::=:==;::==::;==~I =====s\l I t; I ND I I c; I ND I 1,3-Oichlorobenzene I IIbI I s-I I I I I ND I ND I I I I I 1,4-0ichlorobenzene I 1\ IEthyl benzene I \1 ~:..i...;_:....=..::.:..:=.::.:...:..::... _________ -4-__ +--~f-:-----+----:-, --1! I !Toluene I I I ANALYTICAL TEST RESULT (cont'd) l :_, .. '' .. ::···· :·_:::COMPOUNtYti,y·:······· ':'.··:·'··:·':·:·::·::·:::·:·:·:····:···''''<'':/''::'i'Y/: ::"'':':'::::'-'''::f':-<MbtP''':::''l<:-':··:,,MBf'::::::::[::•:·:':\:·:'':"'::,·:7:•I:, :::,·:·:·,::::·:::::::::t:''L':::::--::·:::··:·:·::.:::·il I I ~~:~i!~~=~id• I s I N£> l I I :I IAcetone I I I I I IIIAcroleinIIIIII Acrylonitrile I I I I I I I Bromochloromethane I I I I I In-Butylbenzene I I I I I sec-Butylbenzene I I I I I I Itart-Butylbenzene I I I I !I 12-Chloroethylvinyl ether I I I I ii 12-Chlorotoluene · · 5 I N.D I I I I! I 4-Chlorotoluene I I I I !I Dichlorodifluoromethane I I I I !I I cis-1,2-Dichloroethvlene 5 I ND I I II 1,3-Dichloropropane £" I ND I I II 2,2-Dichloropropane -I I I 11 I I I I 1, 1 -Dichloropropylene I I I 11 Ethylene dibromide (EDS) 5" I ND I I I !I Hexachlorobutadiene I I I I II lsopropylbenzene I I I I Ii p-lsopropyltoluene I I I I !i Methyl Ethyl Ketone I I I I i! Methyl lsobutyl Ketone I I I I i\ Naphthalene ·1 I I I l\ n-Propylbenzene I I I I i\ Styrene I I I I ii 1,2,3-Trichlorobenzene I I I I !\ 1,2,4-Trichlorobenzene I I I I 1,2,4-Trimethylbenzene I I I I 1,3,5-Trimethylbenzene I I I II111. 1,2-Trichloro-trifluoroethane · I I I I IIi Bromofluorobenzene : I ~ I 60-140 I 115' I I I I I I I I I I I I I I I I I I I I I I I I a • R<?ort Any Value > )'.10l..: b • Ustcd Coc,pound, Ace Ordc:-cd by ubor><"')' Alloluc:,l Mc\bcd,: Halo5cn•tcd, Acoc,auc:. tbcn Rccainin5 Coepound, ldc~uficd •y CS::.-:.!S. S?;;: COI-C a SpicingConccntnuon( <5 x POL); AC?~. A<-ce?t.:1blc ~ngc or P_c:-cc~,: r,i::.C .. ~ Rce<>•'C:")' I. I l,!~L a )'.lc:.'>od Octcc:"jcn Uc:iit; MB= Mctbcd Blank: NO c Not Oc,c:::cd (S.low MDL); 1'A a l'\oc Analyze<! I I I I I I I I I I I I I I I I I I I QNQC REPORT Reporting Unit (Circle One):@g)ug/L I. Matrix Spike (MS) Matrix Spike Duplicate (MSD) DATE PERFORMED: 02-13-9, BATCH: q6B04-2 LAB SAMPLE I.D.: BoJJ.2.-0I Benzene 2 7'1-Z2l i3 ~2' B2. r 60-1 LJO LJO Toluene 2. ..,I/-2,.-:z.3 ii 2.2.3 i / O 60-1 LJO LJO Ethylbenzene 2. 7'1-"2. ?:>"! 86 2. 37 16 0 60-1 LJO LJO Total Xvlenes R'2.3 ~., 7'3 5"Cfi 13 O 60-1 LJO 40 II. Laboratory Quality Control Check Sample DATE PERFORMED: 02-/2-96 BATCH: 968Df2 LAB SAMPLE I.D.: VAL!j"87l- Benzene 100.00 82.5"0 80-120 Toluene Jt>0.00 qo. oo 80-120 Ethylbenzene JOO. 00 JOO.SO JO/ 80-120 Total Xylenes 300.00 2.lfi.OO 83 80-120 80-120 80-120 80-120 ANALYST: ~ ,DATE: ~V/76 NOTE: CKY Lab QC limits for LCS/LCSD recoveries: 70-125% I QNQC REPORT I Reporting Unit (Circle One): ~ug/L I I. Matrix Spike (MS) Matrix Spike Duplicate (MSD) I I I I I I I I DATE PERFORMED: BATCH: LAB SAMPLE I.D.: I -. II. Laboratory Quality Control Check Sample DATE PERFORMED: 02-12-'IS ~~____;_;;;__ __ _ BATCH: q(;80J/..2. LAB SAMPLE I.D.: VAL58"/C I I I I . ·· . .:?ANALYJE:: ,<::::>:: x>r=:::se.K:c.oNc#r:rn::RESU 1:::cn1:::rrn::r1t:%':REGOVERYl':::,,:::::::::=Ace:=%: ,.::::r1 I Benzene I 100.00 l i~.oo I. g~ I 80-120 I ·I ! Toluene I 100. oo I 89, 00 I gq I 80-120 I 1 Ethyl benzene I / 00. oo I JOtf~ 00 I /01.f I 80-120 \ I · Total Xylenes I 300. 00 I 2.&I, oo I 'l7 I 80-120 \ I I I I 80-120 I I I I I 80-120 IIjIII80-120 I I ANALYST: I I I NOTE: DATE: CKY Lab QC limits for LCS/LCSD recoveries: 70-125% · I I I I I I I I I I I I ONQC REPORT Reporting Unit (Circle One):~ug/L I. Matrix Spike (MS) Matrix Spike Duplicate (MSD) DATE PERFORMED: BATCH: LAB SAMPLE 1.0.: I I I I : . . . II. Laboratory Quality Control Check Sample DATE PERFORMED: 02-Jt/--C/b _ ____...~'------ BATCH: t:/GBOl/-2.. LAB SAMPLE 1.0.: -VALirl'7L- ANALYJE:t•r::<(:,::(\f:)IfSR.K:GONG#l\'?RESULTtt:@t?l#:%'REGOVERY:l\:t/fACPt%tt>>I I I I I \ Benzene I 100.00· I 'f0.00 ). f/0 ) 80-120 ·1 Toluene · I /DO, 00 I C/1. SO I </2. I 80-120 I Ethylbenzene I /00.00 I gg,S'D I fq I 80-120 I I Total Xylenes I 300.00 I 2'f0. 00 I go I 80-120 I I I I I ! 80-120 I I -I I I 80-120 I I l!:::I =======!=========' ======' ====='=8=0=-=12=0====.!' I ANALYST: ~ ~ DATE: Y/~vf? 6 I I I NOTE: CKY Lab QC limits for LCS/LCSD recoveries: 70-125%. I I I I I I I I I I I I 1 I I I I I I QNQC REPORT Reporting Unit (Circle One):~ug/L I. Matrix Spike (MS) Matrix Spike Duplicate (MSD) DATE PERFORMED: BATCH: LAB SAMPLE 1.0.: II. Laboratory Quality Control Check Sample DATE PERFORMED: 02-/'l--'IG BATCH: qGB0'/-2 LAB SAMPLE 1.0.: VAL.~q7C 1.·• .... ::ANALYTE: > Benzene 100.00 g7,oo 8'r 80-120 Toluene 100. 00 8'8. S"O gg 80-120 Ethyl benzene 100.00 'f6. 5"0 f/T 80-120 Total Xylenes 300.00 232.00 7~ 80-120 I 80-120 80:....120 80-120 ANALYST: DATE: NOTE: CKY Lab QC limits for LCS/LCSD recoveries: 70-125% I I I I I I I I I I I I I I I I I I I APPENDIX C USE OF A GEO FLOWMETER FOR THE DETERMINATION OF GROUND WATER FLOW DIRECTION I I I I I I I I I 1 I I I I I I I I I 1. Reference: Guthrie, M., "Use of a Geo Flowmeter for the Determination of Ground Water Flow/ Ground Water Monitoring Review, Vol. 6, No. 1, 1986, pp. 81-86. Use of a Geo Flowmetel for the Determination of Ground Water Flow Direction by Marilyn Guthrie Abstract The Geo Flowmeter is manufactured by K. V. Asso- ciates of Falmouth. Massachusetts, and is used to determine ground water flow direction and velocity In monitoring wells or open boreholes. It operates by emitting heat pulses and measuring subsequ~nt temperature Increases carried by the ground water movement. The meter can be used In wells as small as 2 Inches in diameter and only a single well ls required for determination ofground water fiow ~lrectlon and rate. This paper ls a case hlstoiy of the use of the Geo Flowmeter In a complex hydrogeologic settingconsist- Ing ofa partially above ~delandfill located between a navigable waterwayand a large stormwater lmpound- ment basin. Mounding effects of the landfill. tidal changes in the channel, varying water levels In the lmpoundment basin and a complex substrate. (alter- nating layers of sand, silt and clay) presented a chal- lenge for ground water Interpretation and analysis. The Geo Flowmeter was lowered into existing moni- toring wells surrounding the landfill to determl~e groundwaterfiowdlrect1onandrate.Sens1tlvityofthe ineter was sufficient to distinguish two separate fiow directions in a single well screen. Later investigation involving lns~tlonofpiezometets. long-teim ground water l~vel monitoring and plotting ~f gro~d water tontows verified lnltlal findings of the meter. This article presents numerous graphs and pic- tures to illustrate .field use ofthe.instrument and dis- cusses advantages ap.d_disadvan~es ofits use.Actual field data collected ls included to provide a basis for evaluating the accuracy ofthe instrument and identi- fying situations w~ere It may be used. Introduction The Geo Flowmeter, manufactured by K. V. Asso- ciates of Falmouth, Massachusetts, ls a portable field · instrument used for determining ground water direc- tion and velocity. Itcan be used in saturated soil. open boreholes and in different size wells. · The instrument op.crates by emitting heat pulses and simultaneously measuring the temperature dif- ferential around tlie circumference of the well. The heat pulses are cari1¢ in one direction by the move- ipent of soil pore water, thus causing.a temperature dUTerentlal. By plotting the measured temperature differentlal in vector fomi. the direction of ground water fiow ls i:ietermlned. K. V. Associat~ has used tlils instrument for mea- suring ground water_ directJQ.I} ~~ yelocity In many dlfferent settings. In one reported case.-borings were made through rock and screened In the sandy till below and the meter was used to predict the deep and shallow flow movement. Studies have also been done to det~ne fiow through lakes and ponds. . .. Thispaperdocumentsuseofthelnstrumentin the. understanding offiow in a complex hydrology setting. Operating princip~~ p~ur:ig.instructlons and sup- porting data documenting its accuracy are also pre- sented. Flnally.advantages and disadvantages ofusing the instrument are presented based on actual field experience. Methods and Materials Fl~ 2.1 shows all the components of the K. V. Associates Geo Flowmi:ter. The instrument operates on the theoiy ofheat movement by the soil pore water as illustrated by Flgure 2.2. The instrument consists of a heat source sur- Spring 1986 81 I I I I I I I I I I I I I I I I I I 00 . --- 0 0 Figure 2.1 Instrument setup for Geo Flowmeter rounded by 10 thermistors. each of which are paired to another making a total of five pair (Figure 2.1 ). The relative thermal difference is displayed, and thesign ( + or·) ofthe value indicates which ofthe two thermistors is reading .the higher _temperature. For example. if thermistor+ l is hotter than its pair, thermistor-6, the display will be a positive value indicating flow (heat) in the direction of+ 1 (Figure 2.2). In a no-flow condition all thermistors see the same temperature rise with time and there is no net differ- ence between pairs (Figure 2.2). Equipment Description Figure 2.3 illustrates how the probe is set up for down the well use. In short. the end cap which contains glass beads is attached to the probe and the probe is then suspended in the well by nylon rods. The compass tee is then attached to the last rod for orientation purposes. . The diameter of the well will determine the type of attachment that must be placed on the end of the probe. The first type of attachment. useful only in 2-inch wells, is called an end cap and consists ofa grey netting filled with glass beads (Figure 2.1 ). This end cap is attached directly to the probe with two small screws and surrounds the probe with a loose porous medium (the glass beads). The second type ofattach-. ment is called a fuzzy packer and can be used in 2~. 4-and 6-inch_wells. The fuzzy packer is a cylinderwith a fuzzy covering made to fit tightly down a well (Figure 2.1 ). This cylinder is also filled with small glass beads to provide a porous medium through which the flow Will stabilize (Figure 2.1). The fuzzy packer also at- taches with two mounting screws directly to the probe. The probe is suspended in the well by the 5-foot nylon suspension rods which join together by srtap buttons (Figure 2.3). The probe is then lowered down the well until it is at the depth ofthe screen. Care must be taken to be sure that the probe is set in the screen of the well and not just in the water. (It is necessary to know the depth of the screen before heading to the field.) Using a pipe ring to hold the nylon tubing, the probe can be suspended at a certain depth. Once the probe is set at the properdepth. itmust be oriented to north. To facilitate this, the compass ls placed on the top most attached nylon rod and snapped in (Figure 2.1 ). The snap attachment ensures that the number + 1 probe ts lined up with the north reading on the compass. When the compass arrow ts oriented toward the north, the probe ls ready for use. 82 Spring 1986 Figure 2.2 Concept of now through pore spaces in soil and Geo Flowmeter now conditions · PO• W&LL UH a•ouND i.1·nL IOLID PYC COUUI IAND ILOTTID PYC SCRHN Figure 2.3 Downwell setup for the Geo Flowmeter Operating Procedure The rotary switch selects which pair ofthermistors are being read and displayed. (Figure 2.4. #5.l The flow rate and direction indicator by + or -is displayed on the LCD (liquid crystal display) as the rotary switch is moved from channel to channel. Readings for each channel should be monitored at short intervals until a stable display is observed. Values should be within +10, however, they may be larger with a greater sensitivity setting. Values for the five channels are recorded on a Ground Water Flow Work- sheet in Column A. as iliustrated in Figure 2.5. After pressing the START button, the LED will flash to indi- cate that a measurement cycle ls In pr!)gress. When the beeper sounds (1 Yi minutes for Model 30), values from respective channels in the .. end" column Bare immediately recorded. The RESET button can be pressed to silen~ the beeper. Next. the probe must be oriented In the south direction again allowing at least five minutes for heat to dissipate and now to re-establish. It is suggested that the fuzzy packer be raised and lowered several times tn order to help the heat dissipate. After five I I I I I I I I I I I I I I I I I I I IC•V ASSOCIAflS INC.. , ... un 20 GIOPl~.. "+ 008 11o,.....i .. ,. ,........ U ~ 4 rn " S··· .... 0) ..... 0 .. ... OPERATING CONTROLS. SOURCI: IC-V A880CIATII INC. G) @ @ @ @ @ @ Function j lwtldi •NIIH .. IIHIH le le1&._..I u .. •• cs11nal '-11•'7 ca.raer. n.. ,. .... Ml< .... ,. ••••--• c,.11 ... .... ,., .. . LID fl1e1M1 ...... N .. l•1 u-•I ...... _. .... , ... . Instruction j 1e.., • u, ...... ·"· ., ""·'· 1, •• . ..... . -· ........ ,. ........ . ............. ,. .. . HINH ,ar .. u... •••• INeH .......... , ... He.II ,. .. u •• ..... , ' ,. ..... , .,,. .. , ............. .. .......................... , ... . u. 111111" nHI ,....... ,. ... le Hffl .. , .. r •• l1&U'n,1 ar-•I c,-le I• ,rec•••• 1) 1,-• ewll•a. .. J••U nulll•Ur. 1) IP ..... •a-.. tih-1 U• M11t ... 11111t1p. 1 u, .... , -hl•&•n ,,.. ,. .. •ff• •> A4Jn1 ... u clec~wh• IIM ••l••-•U le .... 1WUcl1 l•"h• IN•HM •••1lll•llp. n-. ............ ,. ........ , • ........ u .............. . t'Y ........ . t•J Figure 2.4 Operating controls tor the KV Associates Geo Flowmeter minutes the cycle can be repeated and readings recorded in the second set of columns. Column B is then subtracted from Column Aand the results placed in. Column N (or C) as shown in Figure 2.5: repeating the procedure in Column S. Then Column S Is sub- tracted from Column N and divided by 2 (the result is recorded in Column F). Each reading in Column F is then divided by the largest absolute value in this cohimn. Vectors can then be drawn on the circular diagram on the right side of the worksheet for each value with the largest value being I. Then starting at the end of the largest vector, draw vectors head to tail. keeping their respective lengths and directions the same. After redrawing the four other vectors. a line drawn from the center through the head of the last vector will intersect the outermost circle of the paper at a degree reading representing the principal direc- tion of flow. This instrument was also used in open core bor- ings. In this case the prongs of the probe are inserted directly into the soil and readings taken as before. If the bottom of the hold consists of clay. placement of the probe may be difficult since the nylon rods bend easily. When the probe is rotated to the south, it is suggested that the probe be pulled completely from the hole and sediment removed from between the prongs of the probe. Velocity ofthe ground water movement can also be computed as follows: Ne x FL= feet/day through (VG) glass beads Where: Ne = Calibration number FL = Largest value in the Column F (worksheet) y._e1.._ __ o., •. ZS : ........ 92 Statioft1 ___ ._ __ Tiffle1 -10: •:! LocatiM, 'aN& ?aN? ---· ... ,,.1, C,!1!!! ..:: ='"<:5Y"'""" .. f'pp ..................... ............. JI .............. ............. .. u.,....... ........ ,-. ....... . an.-. u ... .. Mfte ................. ... ~ u.. .. ..... @• Yector RnotuUon to O•tenni,.. OlrecUon a&, .... MIIU-Pnt,r-le• n•tl .. , .. i. .. n a ... , .. , ........ ., .., ,.,.., .. , , .. ,.,,_, -... , u.. llff ___ , .................. u..,. 1lalOcft7 Del ....... _ ................. .._ ................... .. ......... ...... .. .... , .... '"· ... ..,,. 1Dlrectloft• ,,. v.tocity• 1A tM. c..,...-1911 IC-V &lf0S1Aftl, INC, , •• ..,,,.. IU 01HD ~, ,, .. Figure 2.5 Ground water flow worksheet Spring 1986 83 4. I I I I I I I I I I I I I I I I I I I Then, using the ratio: 33. PS -v-Va S Where: 33 = the void space of the glass beads Va = feet/day through glass beads. V5 = feet/day through the soil Ps = porosityofsoilcalculated byfillingagraduated cyiinderwith 25 ml ofwaterand then dumping soil into the water until the soil height reaches 25 ml. Then dividing the difference by the old measurement {25 ml) to compute void space. Case History Figure 3.1 shows a specific site layout where the KV-Meter was used for investigative purposes. The site under investigation is an above grade landfill, approximately two {2) acres in size. It is located adja- cent to an intercoastal waterway. Ground waterin this area is affected by tidal changes and the water level in a storm water impoundment The geology of the area is made up ofrelatively complex: river deposits ofalter- nating layers of sand, silt and clay {Figure 3.2) Concern over the area began with the installation ofWell-A (Figure 3.1) Initial and later tests showed low pHs in this well and the source of the low pH was unknown. No record of what was deposited in the landfill was available and manypipelines run through this area making source determination difficult A second well, Well-B. was placed near the storm water impoundment (Figure 3.1) but showed a relatively normal ph of 6 units. i i 1t1Utana,1n1e11111m Figure 3.2 Subsunace cross section of above grade landfill 84 Spring 1986 I Figure 3.1 Geo Flowmeter site map The Geo Flowmeterwas inserted in these two wells and the resultant readings are shown on Figure 3 3. The shallow reading (13 feet) in Well-A and the deep reading {25 feet) showed ground water flow to be in the direction of the water way. However. the shallow read- ing in Well-B showed flow to be in the direction of the storm water impoundment basin. A series of new wells (Figure 3.4) were installed in order to determine the presence of contamination. From the new wells and the reading from -the Geo Flowmeter. flow lines were drawn on a cross section to show the shallow and deep flow directions as shown in Figure 3.5: the above grade landfill is causing a slight 1ttanm,.....,..n..,. a ••• .... " ..... a-- 11 -· ·-- a .. _ ......... _ .... " .. .. · v ._... .... , ..... I I I I I I I I I I I I I I I I I I I i 1 I I -· 5 Spring 1986 85 APR 10 '96 16:30 K-V ASSOCIATES I moundir.g effect. Further. the storm water basin is continually pumped dry causing the local gradient to beloward the basin. However, the underlying regional gradient is toward the waterway. . I . Addluonal evidence to support the effects of the stonn water basin was gathered from continual watu level mo~ftors placed ln the basln. Well-A. Well·B and the water. way. As rainfall was collected and the water I level or the basin increased. Well·B adfusted accord· lng1y. On the other hand. Well-A was affected directly by the rising and falling of the waterway. I Conclusions The .Oeo .Fiowmeter is very appealing because It ts portable and easy to use once operation ofthe tnstnl- ment is mastered. Jt Is sensitive enough to gtve read- I tngs of two different directions in a single screen and ftssensitfvify to local ground waterflows makes It very attractive. Regional ground water flows derived from we,llsmaymtsslocalsttuatlonswhtchmaybeimportant I in· analysts of underground storage facility settings. When compared to an extensive drilling program. it iS relatively tnexpenSive. ln addition. much 1n(ormatlon I can be derived by using the instrument and onlya few wells. Disadvantages would tndude the time and eff'orUt takes to understand and use the tnsuument properly. ne operating manual certainly needs to be more I explicit. It must also be remembered that tn many caees ~ meterwill indicate a verylocal situation that could be is~bject to change. For example. the flow in some wells actually reversed because of tidal sttua- 1 uons.Not all readings taken during the testing or this tnsuument were 100 percent convincing. particularly those taken iii open boreholes. In a deep boring. it was I veiydifftcult to determine ifthe instrumentwas placed In the. soil ccirrectly. I I I I I 1 P.2/2 Acknowledgments Support for the landfill study was pl"OYided by ERM-Southwest Inc; Suggestions regarding the ground water ln'W:Stigatlon. and for lmprovlng tpe manusc:rtpt were~ byMUce Pisan1 ofERM-South- wesL Re1ere1l(:es K. v. A~lates Inc. 1982. Ground Water F1owmeter System-operauons and Maintenance ~ual. K.V. Assodates. F~outh. Massachusetts. B1ogtapb1ca1 Sketeh Ma.rilynGu~i.s em,,l.o.fled.'bytheARCOPetro- lewn Prodw:ta c;o. and is uwolued in geologu; irwes~ttons. ~ water monitoring. hydro- carbon recovery and.RCRAJ~ cit the Hous- ton Refulerv in Houston. Ti!X'CIS. This arti.c.le was written as a result qfthe cw:thor's ~ewith the Geo Plounneter tit the "!;rinery. Gutlu'fe Is c:tgraduateqfBo.ylor Vnwemq, uritha bachelor qfscfence bl geok'){JJJ. (}j)J)er lePel class- work wa.s CO'"l'let.ed bl hyd.rogeol.ogy and hydn;,l~ ogy; ~acluate thesis dealt with the swjm;e welterproblems q/a umin iVaco. Tems. Graduate worlc is currenti,, being com,>let.ed m the Unwer.sity ojHoustorL II ..., ....... 0-. ...... .... . .... .. ............. Ficru,re ·3.5 Su!mmac:e · aoss section with flow liDes of above grade landflD Spring 1986 DEH-9098 (Rev. 10/15) Request # County of San Diego DEPARTMENT OF ENVIRONMENTAL HEALTH P.O. BOX 129261, SAN DIEGO, CA 92112 -9261 858) 505 -6700 FAX (858) 505-6848 www.sdcdeh.org PUBLIC RECORDS REQUEST FOR THE SITE ASSESSMENT AND MITIGATION (SAM) PROGRAM AND HAZARDOUS MATERIALS DIVISION (HMD) Requestor Name: Sara Gengler E-Mail: RedactorsInk@yahoo.com Phone: ( 702 ) 240-9689 FAX: ( ) Company Name: Redactors Ink Mailing Address: 237 Fowles St., Oceanside, CA 92054 You may attach a business card/overprint with business card if preferred) Additional information may be accessed from the DEH website, www.sdcdeh.org. Fax or email your completed form to the Public Records Program at (858) 505-6848 or deh.publicrecords@sdcounty.ca.gov. The following information is required. Separate forms are needed for each address or parcel number. 517 Shinohara Lane, Chula Vista, CA 91911 or 644-040-01-00 Exact Address (Street, City and Zip Code) Assessor Parcel Number Optional information (establishment permit number, business name, etc.): Please indicate the purpose of your search by checking all that apply: Contaminated Property Investigation(s) (SAM Cases) SAM Closure Letter/Report Hazardous Materials Permit & Underground Storage Tank Files (HMD/UST) Other (specify): Monitoring Well Files OFFICE USE ONLY BELOW THIS LINE Files reviewed by: of Date: Files copied for: of Date: Request cancelled by: Date: Photocopies Cost Picked up/mailed on By A search for DEH records checked above has been conducted and the following apply: SAM files for the permit number(s) listed below are available. HMD/UST files for the permit number(s) listed below are available. Original records were purged. No SAM/HMD/UST records were found for the address/APN you requested. Signature - DEH Representative Date DEH complies fully with the California Public Records Act and the Federal Freedom of Information Act. Please be advised that photocopy and/or scanned file fees may apply. July 2014 http://www.fema.gov/rm-main · 1–877–FEMA MAP FEMA Digital Flood Map Products FIRM Panel Image: Flood Insurance Rate Maps (FIRM) are digital images of flood hazard maps. The images are digital pictures of entire flood map panels that can be viewed and printed from a computer. Most communities and counties have many map panels to cover the entire jurisdiction and an index map that shows the location of each map panel. FIRM Worldfile: A TFW or PGW file may accompany your flood hazard map. They are used to help view the flood maps in GIS applications. FIRM Panel Images are TIF or PNG image files and have file names with a Community or County ID followed by a 4-digital panel number and letter suffix representing a version (e.g. 12345C0123F.tif). The FIRM worldfiles will have the same filenames but with a .tfw or .pgw extension. FIRM Panel Images can be viewed using most freely available image viewer applications. You can also use the FIRMette-Desktop software available from the FEMA Flood Map Service Center (MSC) website at msc.fema.gov/portal/resources/firmettes. FIRM images can also be viewed in specialized GIS software where the worldfiles are used to make the images compatiable with other GIS data. See the MSC Products and Tools Overview page for more information on avialable data and tools for using FEMA’s flood risk data. For more information on available digital products, visit FEMA’s Map Service Center website at https://msc.fema.gov or call the FEMA Map Information eXchange (FMIX) at 877-336-2627. APPENDIX C: REGULATORY DATABASE REPORT FORM-LBC-ASH kcehCoeGhtiwtropeR ™paMsuidaRRDEehT 6 Armstrong Road, 4th floor Shelton, CT 06484 Toll Free: 800.352.0050 www.edrnet.com Industrial Land 517 Shinohara Lane Chula Vista, CA 91911 Inquiry Number: 5146125.2s December 27, 2017 SECTION PAGE Executive Summary ES1 Overview Map 2 Detail Map 3 Map Findings Summary 4 Map Findings 8 Orphan Summary 167 Government Records Searched/Data Currency Tracking GR-1 GEOCHECK ADDENDUM Physical Setting Source Addendum A-1 Physical Setting Source Summary A-2 Physical Setting SSURGO Soil Map A-6 Physical Setting Source Map A-13 Physical Setting Source Map Findings A-15 Physical Setting Source Records Searched PSGR-1 TC5146125.2s Thank you for your business. Please contact EDR at 1-800-352-0050 with any questions or comments. Disclaimer - Copyright and Trademark Notice This Report contains certain information obtained from a variety of public and other sources reasonably available to Environmental Data Resources, Inc. It cannot be concluded from this Report that coverage information for the target and surrounding properties does not exist from other sources. NO WARRANTY EXPRESSED OR IMPLIED, IS MADE WHATSOEVER IN CONNECTION WITH THIS REPORT. ENVIRONMENTAL DATA RESOURCES, INC. SPECIFICALLY DISCLAIMS THE MAKING OF ANY SUCH WARRANTIES, INCLUDING WITHOUT LIMITATION, MERCHANTABILITY OR FITNESS FOR A PARTICULAR USE OR PURPOSE. ALL RISK IS ASSUMED BY THE USER. IN NO EVENT SHALL ENVIRONMENTAL DATA RESOURCES, INC. BE LIABLE TO ANYONE, WHETHER ARISING OUT OF ERRORS OR OMISSIONS, NEGLIGENCE, ACCIDENT OR ANY OTHER CAUSE, FOR ANY LOSS OF DAMAGE, INCLUDING, WITHOUT LIMITATION, SPECIAL, INCIDENTAL, CONSEQUENTIAL, OR EXEMPLARY DAMAGES. ANY LIABILITY ON THE PART OF ENVIRONMENTAL DATA RESOURCES, INC. IS STRICTLY LIMITED TO A REFUND OF THE AMOUNT PAID FOR THIS REPORT. Purchaser accepts this Report "AS IS". Any analyses, estimates, ratings, environmental risk levels or risk codes provided in this Report are provided for illustrative purposes only, and are not intended to provide, nor should they be interpreted as providing any facts regarding, or prediction or forecast of, any environmental risk for any property. Only a Phase I Environmental Site Assessment performed by an environmental professional can provide information regarding the environmental risk for any property. Additionally, the information provided in this Report is not to be construed as legal advice. Copyright 2017 by Environmental Data Resources, Inc. All rights reserved. Reproduction in any media or format, in whole or in part, of any report or map of Environmental Data Resources, Inc., or its affiliates, is prohibited without prior written permission. EDR and its logos (including Sanborn and Sanborn Map) are trademarks of Environmental Data Resources, Inc. or its affiliates. All other trademarks used herein are the property of their respective owners. TABLE OF CONTENTS EXECUTIVE SUMMARY TC5146125.2s EXECUTIVE SUMMARY 1 A search of available environmental records was conducted by Environmental Data Resources, Inc (EDR). The report was designed to assist parties seeking to meet the search requirements of EPA’s Standards and Practices for All Appropriate Inquiries (40 CFR Part 312), the ASTM Standard Practice for Environmental Site Assessments (E 1527-13), the ASTM Standard Practice for Environmental Site Assessments for Forestland or Rural Property (E 2247-16), the ASTM Standard Practice for Limited Environmental Due Diligence: Transaction Screen Process (E 1528-14) or custom requirements developed for the evaluation of environmental risk associated with a parcel of real estate. TARGET PROPERTY INFORMATION ADDRESS 517 SHINOHARA LANE CHULA VISTA, CA 91911 COORDINATES 32.5973850 - 32 35’ 50.58’’Latitude (North): 117.0315190 - 117 1’ 53.46’’Longitude (West): Zone11UniversalTranverseMercator: 497042.2UTMX (Meters): 3606465.2UTMY (Meters): 204 ft. above sealevelElevation: USGS TOPOGRAPHIC MAP ASSOCIATED WITH TARGET PROPERTY 5622818 IMPERIAL BEACH, CATargetPropertyMap: 2012VersionDate: AERIAL PHOTOGRAPHY IN THIS REPORT 20140805PortionsofPhotofrom: USDASource: 5146125.2s Page 2 I31 APPROPRIATE TECHNOLO 1700 MAXWELL RD SEMS-ARCHIVE, CORRACTS, RCRA-TSDF, RCRA-SQG, 2020...Higher 4792, 0.908, ENE I30 APPROPRIATE TECHNOLO 1700 MAXWELL RD CA ENVIROSTOR, CA SWF/LF, CA LDS, CA ENF, CA... Higher 4792, 0.908, ENE I29 ALLIED WASTE - OTAY 1700 MAXWELL ROAD CA SWF/LF, CA San Diego Co. HMMD, CA HIST UST, CA... Higher 4792, 0.908, ENE I28 OTAY SANITARY LANDFI OTAY VALLEY ROAD CA ENVIROSTOR Higher 4773, 0.904, ENE 27 APACHE SERVICES 4551 OTAY VALLEY ROA CA ENVIROSTOR, CA BOND EXP. PLAN Lower 4038, 0.765, WSW 26 DAVIES PROPERTY NO ADDRESS US BROWNFIELDS Lower 2112, 0.400, SSW H25 VINCENT DAVIES PROPE 4501 OTAY VALLEY ROA SEMS-ARCHIVE Lower 2016, 0.382, ESE H24 VINCENT DAVIES PROPE 4501 OTAY VALLEY ROA CA ENVIROSTOR, CA SLIC, CA San Diego Co. HMMD, CA... Lower 2016, 0.382, ESE 23 ARCO 4430 OTAY VALLEY RD CA LUST Lower 1914, 0.363, WSW 22 SHINOHARA II PROPERT S OF 4700 BLK. MAIN CA SWF/LF Lower 1735, 0.329, South 21 FORMER OMAR RENDERIN 1886 AUTO PARK PLACE CA DEED, CA LDS, CA BOND EXP. PLAN, CA Cortese, CA... Lower 1325, 0.251, East G20 PEOPLES CHEVROLET 580 AUTO PARK DR RCRA-SQG, CA AST, CA San Diego Co. HMMD, FINDS,... Lower 1125, 0.213, SE F19 KIDDIE KANDIDS #0060 4501 MAIN STREET RCRA-SQG Lower 1122, 0.213, SW G18 FORMER DARLING INTL 4826 AUTO PARK DR RCRA-SQG, CA HAZNET Lower 1077, 0.204, SE F17 OTAY VALLEY SHELL SV 455 OTAY VALLEY RD CA HIST UST Lower 1071, 0.203, SW E16 SHELL 4555 AUTO PARK DR CA LUST, CA SAN DIEGO CO. SAM Lower 982, 0.186, SW F15 SHELL OIL INC 4555 OTAY VALLEYRD CA SWEEPS UST Lower 965, 0.183, SW E14 S & L SHELL MART 4555 MAIN ST CA UST Lower 936, 0.177, SW E13 PACIFIC BELL 490 OTAY VALLEY RD CA LUST, CA SAN DIEGO CO. SAM, CA SWEEPS UST, CA... Lower 763, 0.145, SW 12 RAYCHEM CORP 1669 BRANDYWINE AVE RCRA NonGen / NLR, FINDS, ECHO, CA HAZNET Higher 751, 0.142, East D11 FULLER FORD HONDA 560 AUTO PARK DR RCRA-SQG, FINDS, ECHO, CA EMI, CA HAZNET Lower 736, 0.139, SSE D10 FULLER FORD/KIA 540 AUTO PARK DR CA AST, CA San Diego Co. HMMD Lower 727, 0.138, South D9 FULLER FORD/HONDA 540/560 AUTO PARK DR CA AST Lower 727, 0.138, South C8 ANTEON CORPORATION 1675 BRANDYWINE STE RCRA-CESQG, FINDS, ECHO Lower 706, 0.134, ESE C7 CODE A PHONE CORP 1675 BRANDYWINE AVE RCRA-SQG, FINDS, ECHO, CA HAZNET Lower 706, 0.134, ESE C6 DRESSER-RAND REAPIR 1675 BRANDYWINE AVEN RCRA-LQG Lower 706, 0.134, ESE 5 JO-BIE PRODUCTS COMP 516 TALLOW CT RCRA-SQG, FINDS, ECHO Higher 697, 0.132, NNW B4 HYSPAN PRECISION PRO 1685 BRANDYWINE AVE CA HIST UST Lower 573, 0.109, SE B3 HYSPAN PRECISION PRO 1685 BRANDYWINE AVE CA SWEEPS UST Lower 573, 0.109, SE A2 BRANDYWINE DISTRIBUT 1670 & 1690 BRANDYWI CA SLIC Lower 261, 0.049, ESE A1 BRANDYWINE DISTRIBUT 1670 & 1690 BRANDYWI CA WMUDS/SWAT Lower 92, 0.017, ESE MAPPED SITES SUMMARY Target Property Address: 517 SHINOHARA LANE CHULA VISTA, CA 91911 Click on Map ID to see full detail. MAP RELATIVE DIST (ft. & mi.) ID DATABASE ACRONYMS ELEVATIONDIRECTIONSITENAMEADDRESS EXECUTIVE SUMMARY TC5146125.2s EXECUTIVE SUMMARY 3 TARGET PROPERTY SEARCH RESULTS The target property was not listed in any of the databases searched by EDR. DATABASES WITH NO MAPPED SITES No mapped sites were found in EDR’s search of available ("reasonably ascertainable ") government records either on the target property or within the search radius around the target property for the following databases: STANDARD ENVIRONMENTAL RECORDS Federal NPL site list NPL National Priority List Proposed NPL Proposed National Priority List Sites NPL LIENS Federal Superfund Liens Federal Delisted NPL site list Delisted NPL National Priority List Deletions Federal CERCLIS list FEDERAL FACILITY Federal Facility Site Information listing SEMS Superfund Enterprise Management System Federal institutional controls / engineering controls registries LUCIS Land Use Control Information System US ENG CONTROLS Engineering Controls Sites List US INST CONTROL Sites with Institutional Controls Federal ERNS list ERNS Emergency Response Notification System State- and tribal - equivalent NPL CA RESPONSE State Response Sites State and tribal leaking storage tank lists INDIAN LUST Leaking Underground Storage Tanks on Indian Land State and tribal registered storage tank lists FEMA UST Underground Storage Tank Listing INDIAN UST Underground Storage Tanks on Indian Land EXECUTIVE SUMMARY TC5146125.2s EXECUTIVE SUMMARY 4 State and tribal voluntary cleanup sites CA VCP Voluntary Cleanup Program Properties INDIAN VCP Voluntary Cleanup Priority Listing State and tribal Brownfields sites CA BROWNFIELDS Considered Brownfieds Sites Listing ADDITIONAL ENVIRONMENTAL RECORDS Local Lists of Landfill / Solid Waste Disposal Sites CA SWRCY Recycler Database CA HAULERS Registered Waste Tire Haulers Listing INDIAN ODI Report on the Status of Open Dumps on Indian Lands DEBRIS REGION 9 Torres Martinez Reservation Illegal Dump Site Locations ODI Open Dump Inventory IHS OPEN DUMPS Open Dumps on Indian Land Local Lists of Hazardous waste / Contaminated Sites US HIST CDL Delisted National Clandestine Laboratory Register CA HIST Cal-Sites Historical Calsites Database CA SCH School Property Evaluation Program CA CDL Clandestine Drug Labs CA Toxic Pits Toxic Pits Cleanup Act Sites US CDL National Clandestine Laboratory Register Local Lists of Registered Storage Tanks CA FID UST Facility Inventory Database Local Land Records CA LIENS Environmental Liens Listing LIENS 2 CERCLA Lien Information Records of Emergency Release Reports HMIRS Hazardous Materials Information Reporting System CA CHMIRS California Hazardous Material Incident Report System CA MCS Military Cleanup Sites Listing CA SPILLS 90 SPILLS 90 data from FirstSearch Other Ascertainable Records FUDS Formerly Used Defense Sites DOD Department of Defense Sites SCRD DRYCLEANERS State Coalition for Remediation of Drycleaners Listing US FIN ASSUR Financial Assurance Information EPA WATCH LIST EPA WATCH LIST TSCA Toxic Substances Control Act EXECUTIVE SUMMARY TC5146125.2s EXECUTIVE SUMMARY 5 TRIS Toxic Chemical Release Inventory System SSTS Section 7 Tracking Systems ROD Records Of Decision RMP Risk Management Plans RAATS RCRA Administrative Action Tracking System PRP Potentially Responsible Parties PADS PCB Activity Database System ICIS Integrated Compliance Information System FTTS FIFRA/ TSCA Tracking System - FIFRA (Federal Insecticide, Fungicide, & Rodenticide Act)/TSCA (Toxic Substances Control Act) MLTS Material Licensing Tracking System COAL ASH DOE Steam-Electric Plant Operation Data COAL ASH EPA Coal Combustion Residues Surface Impoundments List PCB TRANSFORMER PCB Transformer Registration Database RADINFO Radiation Information Database HIST FTTS FIFRA/TSCA Tracking System Administrative Case Listing DOT OPS Incident and Accident Data CONSENT Superfund (CERCLA) Consent Decrees INDIAN RESERV Indian Reservations FUSRAP Formerly Utilized Sites Remedial Action Program UMTRA Uranium Mill Tailings Sites LEAD SMELTERS Lead Smelter Sites US AIRS Aerometric Information Retrieval System Facility Subsystem US MINES Mines Master Index File ABANDONED MINES Abandoned Mines DOCKET HWC Hazardous Waste Compliance Docket Listing UXO Unexploded Ordnance Sites FUELS PROGRAM EPA Fuels Program Registered Listing CA CUPA Listings CUPA Resources List CA DRYCLEANERS Cleaner Facilities CA ICE ICE CA HWT Registered Hazardous Waste Transporter Database CA MINES Mines Site Location Listing CA MWMP Medical Waste Management Program Listing CA PEST LIC Pesticide Regulation Licenses Listing CA PROC Certified Processors Database CA Notify 65 Proposition 65 Records CA UIC UIC Listing CA WASTEWATER PITS Oil Wastewater Pits Listing CA WDS Waste Discharge System CA WIP Well Investigation Program Case List EDR HIGH RISK HISTORICAL RECORDS EDR Exclusive Records EDR MGP EDR Proprietary Manufactured Gas Plants EDR Hist Auto EDR Exclusive Historical Auto Stations EDR Hist Cleaner EDR Exclusive Historical Cleaners EDR RECOVERED GOVERNMENT ARCHIVES Exclusive Recovered Govt. Archives CA RGA LF Recovered Government Archive Solid Waste Facilities List EXECUTIVE SUMMARY TC5146125.2s EXECUTIVE SUMMARY 6 CA RGA LUST Recovered Government Archive Leaking Underground Storage Tank SURROUNDING SITES: SEARCH RESULTS Surrounding sites were identified in the following databases. Elevations have been determined from the USGS Digital Elevation Model and should be evaluated on a relative (not an absolute) basis. Relative elevation information between sites of close proximity should be field verified. Sites with an elevation equal to or higher than the target property have been differentiated below from sites with an elevation lower than the target property. Page numbers and map identification numbers refer to the EDR Radius Map report where detailed data on individual sites can be reviewed. Sites listed in bold italics are in multiple databases. Unmappable (orphan) sites are not considered in the foregoing analysis. STANDARD ENVIRONMENTAL RECORDS Federal CERCLIS NFRAP site list SEMS-ARCHIVE: SEMS-ARCHIVE (Superfund Enterprise Management System Archive) tracks sites that have no further interest under the Federal Superfund Program based on available information. The list was formerly known as the CERCLIS-NFRAP, renamed to SEMS ARCHIVE by the EPA in 2015. EPA may perform a minimal level of assessment work at a site while it is archived if site conditions change and/or new information becomes available. Archived sites have been removed and archived from the inventory of SEMS sites. Archived status indicates that, to the best of EPA’s knowledge, assessment at a site has been completed and that EPA has determined no further steps will be taken to list the site on the National Priorities List (NPL), unless information indicates this decision was not appropriate or other considerations require a recommendation for listing at a later time. The decision does not necessarily mean that there is no hazard associated with a given site; it only means that. based upon available information, the location is not judged to be potential NPL site. A review of the SEMS-ARCHIVE list, as provided by EDR, and dated 07/11/2017 has revealed that there is 1 SEMS-ARCHIVE site within approximately 0.5 miles of the target property. PageMapIDDirection / DistanceAddressLowerElevation ____________________ ________ ___________________ _____ _____ VINCENT DAVIES PROPE 4501 OTAY VALLEY ROA ESE 1/4 - 1/2 (0.382 mi.) H25 95 Federal RCRA CORRACTS facilities list CORRACTS: CORRACTS is a list of handlers with RCRA Corrective Action Activity. This report shows which nationally-defined corrective action core events have occurred for every handler that has had corrective action activity. A review of the CORRACTS list, as provided by EDR, and dated 09/13/2017 has revealed that there is 1 CORRACTS site within approximately 1 mile of the target property. PageMapIDDirection / DistanceAddressEqual/Higher Elevation ____________________ ________ ___________________ _____ _____ APPROPRIATE TECHNOLO 1700 MAXWELL RD ENE 1/2 - 1 (0.908 mi.) I31 141 EXECUTIVE SUMMARY TC5146125.2s EXECUTIVE SUMMARY 7 Federal RCRA generators list RCRA-LQG: RCRAInfo is EPA’s comprehensive information system, providing access to data supporting the Resource Conservation and Recovery Act (RCRA) of 1976 and the Hazardous and Solid Waste Amendments (HSWA) of 1984. The database includes selective information on sites which generate, transport, store, treat and/or dispose of hazardous waste as defined by the Resource Conservation and Recovery Act (RCRA). Large quantity generators (LQGs) generate over 1,000 kilograms (kg) of hazardous waste, or over 1 kg of acutely hazardous waste per month. A review of the RCRA-LQG list, as provided by EDR, and dated 09/13/2017 has revealed that there is 1 RCRA-LQG site within approximately 0.25 miles of the target property. PageMapIDDirection / DistanceAddressLowerElevation ____________________ ________ ___________________ _____ _____ DRESSER-RAND REAPIR 1675 BRANDYWINE AVEN ESE 1/8 - 1/4 (0.134 mi.) C6 12 RCRA-SQG: RCRAInfo is EPA’s comprehensive information system, providing access to data supporting the Resource Conservation and Recovery Act (RCRA) of 1976 and the Hazardous and Solid Waste Amendments (HSWA) of 1984. The database includes selective information on sites which generate, transport, store, treat and/or dispose of hazardous waste as defined by the Resource Conservation and Recovery Act (RCRA). Small quantity generators (SQGs) generate between 100 kg and 1,000 kg of hazardous waste per month. A review of the RCRA-SQG list, as provided by EDR, and dated 09/13/2017 has revealed that there are 6 RCRA-SQG sites within approximately 0.25 miles of the target property. PageMapIDDirection / DistanceAddressEqual/Higher Elevation ____________________ ________ ___________________ _____ _____ JO-BIE PRODUCTS COMP 516 TALLOW CT NNW 1/8 - 1/4 (0.132 mi.) 5 10 PageMapIDDirection / DistanceAddressLowerElevation ____________________ ________ ___________________ _____ _____ CODE A PHONE CORP 1675 BRANDYWINE AVE ESE 1/8 - 1/4 (0.134 mi.) C7 17 FULLER FORD HONDA 560 AUTO PARK DR SSE 1/8 - 1/4 (0.139 mi.) D11 38 FORMER DARLING INTL 4826 AUTO PARK DR SE 1/8 - 1/4 (0.204 mi.) G18 57 KIDDIE KANDIDS #0060 4501 MAIN STREET SW 1/8 - 1/4 (0.213 mi.) F19 60 PEOPLES CHEVROLET 580 AUTO PARK DR SE 1/8 - 1/4 (0.213 mi.) G20 62 RCRA-CESQG: RCRAInfo is EPA’s comprehensive information system, providing access to data supporting the Resource Conservation and Recovery Act (RCRA) of 1976 and the Hazardous and Solid Waste Amendments (HSWA) of 1984. The database includes selective information on sites which generate, transport, store, treat and/or dispose of hazardous waste as defined by the Resource Conservation and Recovery Act (RCRA). Conditionally exempt small quantity generators (CESQGs) generate less than 100 kg of hazardous waste, or less than 1 kg of acutely hazardous waste per month. A review of the RCRA-CESQG list, as provided by EDR, and dated 09/13/2017 has revealed that there is 1 RCRA-CESQG site within approximately 0.25 miles of the target property. PageMapIDDirection / DistanceAddressLowerElevation ____________________ ________ ___________________ _____ _____ ANTEON CORPORATION 1675 BRANDYWINE STE ESE 1/8 - 1/4 (0.134 mi.) C8 18 EXECUTIVE SUMMARY TC5146125.2s EXECUTIVE SUMMARY 8 State- and tribal - equivalent CERCLIS CA ENVIROSTOR: The Department of Toxic Substances Control’s (DTSC’s) Site Mitigation and Brownfields Reuse Program’s (SMBRP’s) EnviroStor database identifes sites that have known contamination or sites for which there may be reasons to investigate further. The database includes the following site types: Federal Superfund sites (National Priorities List (NPL)); State Response, including Military Facilities and State Superfund; Voluntary Cleanup; and School sites. EnviroStor provides similar information to the information that was available in CalSites, and provides additional site information, including, but not limited to, identification of formerly-contaminated properties that have been released for reuse, properties where environmental deed restrictions have been recorded to prevent inappropriate land uses, and risk characterization information that is used to assess potential impacts to public health and the environment at contaminated sites. A review of the CA ENVIROSTOR list, as provided by EDR, and dated 10/30/2017 has revealed that there are 4 CA ENVIROSTOR sites within approximately 1 mile of the target property. PageMapIDDirection / DistanceAddressEqual/Higher Elevation ____________________ ________ ___________________ _____ _____ OTAY SANITARY LANDFI OTAY VALLEY ROAD ENE 1/2 - 1 (0.904 mi.) I28 100 Facility Id: 37490031 Status: Refer: RWQCB APPROPRIATE TECHNOLO 1700 MAXWELL RD ENE 1/2 - 1 (0.908 mi.) I30 114 Facility Id: 80001820 Facility Id: 37730291 Status: * Inactive Status: Refer: RCRA PageMapIDDirection / DistanceAddressLowerElevation ____________________ ________ ___________________ _____ _____ VINCENT DAVIES PROPE 4501 OTAY VALLEY ROA ESE 1/4 - 1/2 (0.382 mi.) H24 92 Facility Id: 37730292 Status: Refer: Other Agency APACHE SERVICES 4551 OTAY VALLEY ROA WSW 1/2 - 1 (0.765 mi.) 27 99 Facility Id: 37500032 Status: Refer: RWQCB State and tribal landfill and/or solid waste disposal site lists CA SWF/LF: The Solid Waste Facilities/Landfill Sites records typically contain an inventory of solid waste disposal facilities or landfills in a particular state. The data come from the Integrated Waste Management Board’s Solid Waste Information System (SWIS) database. A review of the CA SWF/LF list, as provided by EDR, has revealed that there is 1 CA SWF/LF site within approximately 0.5 miles of the target property. PageMapIDDirection / DistanceAddressLowerElevation ____________________ ________ ___________________ _____ _____ SHINOHARA II PROPERT S OF 4700 BLK. MAIN S 1/4 - 1/2 (0.329 mi.) 22 90 Database: SWF/LF (SWIS), Date of Government Version: 11/13/2017 Facility ID: 37-CR-0075 Operational Status: Closed Regulation Status: Pre-regulations EXECUTIVE SUMMARY TC5146125.2s EXECUTIVE SUMMARY 9 State and tribal leaking storage tank lists CA SAN DIEGO CO. SAM: The listing contains all underground tank release cases and projects pertaining to properties contaminated with hazardous substances that are actively under review by the Site Assessment and Mitigation Program. A review of the CA SAN DIEGO CO. SAM list, as provided by EDR, and dated 03/23/2010 has revealed that there are 2 CA SAN DIEGO CO. SAM sites within approximately 0.5 miles of the target property. PageMapIDDirection / DistanceAddressLowerElevation ____________________ ________ ___________________ _____ _____ PACIFIC BELL 490 OTAY VALLEY RD SW 1/8 - 1/4 (0.145 mi.) E13 48 Case Number: H14060-001 Facility Status: Closed Case SHELL 4555 AUTO PARK DR SW 1/8 - 1/4 (0.186 mi.) E16 52 Case Number: H02893-001 Facility Status: Remedial Investigation CA LUST: Leaking Underground Storage Tank (LUST) Sites included in GeoTracker. GeoTracker is the Water Boards data management system for sites that impact, or have the potential to impact, water quality in California, with emphasis on groundwater. A review of the CA LUST list, as provided by EDR, has revealed that there are 3 CA LUST sites within approximately 0.5 miles of the target property. PageMapIDDirection / DistanceAddressLowerElevation ____________________ ________ ___________________ _____ _____ PACIFIC BELL 490 OTAY VALLEY RD SW 1/8 - 1/4 (0.145 mi.) E13 48 Database: LUST REG 9, Date of Government Version: 03/01/2001 Database: LUST, Date of Government Version: 09/11/2017 Status: Completed - Case Closed Closed Date: 2/14/91 Status: Case Closed Global Id: T0607300404 Case Number: 9UT1584 SHELL 4555 AUTO PARK DR SW 1/8 - 1/4 (0.186 mi.) E16 52 Database: LUST, Date of Government Version: 09/11/2017 Status: Completed - Case Closed Global Id: T0607367594 ARCO 4430 OTAY VALLEY RD WSW 1/4 - 1/2 (0.363 mi.) 23 91 Database: LUST, Date of Government Version: 09/11/2017 Status: Completed - Case Closed Global Id: T0607313861 CA SLIC: Cleanup Program Sites (CPS; also known as Site Cleanups [SC] and formerly known as Spills, Leaks, Investigations, and Cleanups [SLIC] sites) included in GeoTracker. GeoTracker is the Water Boards data management system for sites that impact, or have the potential to impact, water quality in California, with emphasis on groundwater. A review of the CA SLIC list, as provided by EDR, has revealed that there are 2 CA SLIC sites within approximately 0.5 miles of the target property. EXECUTIVE SUMMARY TC5146125.2s EXECUTIVE SUMMARY 10 PageMapIDDirection / DistanceAddressLowerElevation ____________________ ________ ___________________ _____ _____ BRANDYWINE DISTRIBUT 1670 & 1690 BRANDYWI ESE 0 - 1/8 (0.049 mi.) A2 9 Database: SLIC, Date of Government Version: 09/11/2017 Facility Status: Completed - Case Closed Global Id: L10003764847 VINCENT DAVIES PROPE 4501 OTAY VALLEY ROA ESE 1/4 - 1/2 (0.382 mi.) H24 92 Database: SLIC, Date of Government Version: 09/11/2017 Facility Status: Completed - Case Closed Global Id: T0608113999 State and tribal registered storage tank lists CA UST: The Underground Storage Tank database contains registered USTs. USTs are regulated under Subtitle I of the Resource Conservation and Recovery Act (RCRA). The data come from the State Water Resources Control Board’s Hazardous Substance Storage Container Database. A review of the CA UST list, as provided by EDR, has revealed that there is 1 CA UST site within approximately 0.25 miles of the target property. PageMapIDDirection / DistanceAddressLowerElevation ____________________ ________ ___________________ _____ _____ S & L SHELL MART 4555 MAIN ST SW 1/8 - 1/4 (0.177 mi.) E14 51 Database: UST, Date of Government Version: 09/11/2017 Facility Id: H02893 CA AST: A listing of aboveground storage tank petroleum storage tank locations. A review of the CA AST list, as provided by EDR, and dated 07/06/2016 has revealed that there are 3 CA AST sites within approximately 0.25 miles of the target property. PageMapIDDirection / DistanceAddressLowerElevation ____________________ ________ ___________________ _____ _____ FULLER FORD/HONDA 540/560 AUTO PARK DR S 1/8 - 1/4 (0.138 mi.) D9 20 FULLER FORD/KIA 540 AUTO PARK DR S 1/8 - 1/4 (0.138 mi.) D10 21 PEOPLES CHEVROLET 580 AUTO PARK DR SE 1/8 - 1/4 (0.213 mi.) G20 62 ADDITIONAL ENVIRONMENTAL RECORDS Local Brownfield lists US BROWNFIELDS: The EPA’s listing of Brownfields properties from the Cleanups in My Community program, which provides information on Brownfields properties for which information is reported back to EPA, as well as areas served by Brownfields grant programs. A review of the US BROWNFIELDS list, as provided by EDR, and dated 08/21/2017 has revealed that there is 1 US BROWNFIELDS site within approximately 0.5 miles of the target property. PageMapIDDirection / DistanceAddressLowerElevation ____________________ ________ ___________________ _____ _____ DAVIES PROPERTY NO ADDRESS SSW 1/4 - 1/2 (0.400 mi.) 26 96 EXECUTIVE SUMMARY TC5146125.2s EXECUTIVE SUMMARY 11 Local Lists of Landfill / Solid Waste Disposal Sites CA WMUDS/SWAT: The Waste Management Unit Database System is used for program tracking and inventory of waste management units. The source is the State Water Resources Control Board. A review of the CA WMUDS/SWAT list, as provided by EDR, and dated 04/01/2000 has revealed that there is 1 CA WMUDS/SWAT site within approximately 0.5 miles of the target property. PageMapIDDirection / DistanceAddressLowerElevation ____________________ ________ ___________________ _____ _____ BRANDYWINE DISTRIBUT 1670 & 1690 BRANDYWI ESE 0 - 1/8 (0.017 mi.) A1 8 Local Lists of Registered Storage Tanks CA SWEEPS UST: Statewide Environmental Evaluation and Planning System. This underground storage tank listing was updated and maintained by a company contacted by the SWRCB in the early 1990’s. The listing is no longer updated or maintained. The local agency is the contact for more information on a site on the SWEEPS list. A review of the CA SWEEPS UST list, as provided by EDR, and dated 06/01/1994 has revealed that there are 3 CA SWEEPS UST sites within approximately 0.25 miles of the target property. PageMapIDDirection / DistanceAddressLowerElevation ____________________ ________ ___________________ _____ _____ HYSPAN PRECISION PRO 1685 BRANDYWINE AVE SE 0 - 1/8 (0.109 mi.) B3 9 Status: A Tank Status: A Comp Number: 19570 PACIFIC BELL 490 OTAY VALLEY RD SW 1/8 - 1/4 (0.145 mi.) E13 48 Status: A Comp Number: 14060 SHELL OIL INC 4555 OTAY VALLEYRD SW 1/8 - 1/4 (0.183 mi.) F15 51 Status: A Tank Status: A Comp Number: 2893 CA HIST UST: Historical UST Registered Database. A review of the CA HIST UST list, as provided by EDR, and dated 10/15/1990 has revealed that there are 2 CA HIST UST sites within approximately 0.25 miles of the target property. PageMapIDDirection / DistanceAddressLowerElevation ____________________ ________ ___________________ _____ _____ HYSPAN PRECISION PRO 1685 BRANDYWINE AVE SE 0 - 1/8 (0.109 mi.) B4 10 Facility Id: 00000002098 OTAY VALLEY SHELL SV 455 OTAY VALLEY RD SW 1/8 - 1/4 (0.203 mi.) F17 56 Facility Id: 00000044031 EXECUTIVE SUMMARY TC5146125.2s EXECUTIVE SUMMARY 12 Local Land Records CA DEED: The use of recorded land use restrictions is one of the methods the DTSC uses to protect the public from unsafe exposures to hazardous substances and wastes . A review of the CA DEED list, as provided by EDR, and dated 09/05/2017 has revealed that there is 1 CA DEED site within approximately 0.5 miles of the target property. PageMapIDDirection / DistanceAddressLowerElevation ____________________ ________ ___________________ _____ _____ FORMER OMAR RENDERIN 1886 AUTO PARK PLACE E 1/4 - 1/2 (0.251 mi.) 21 76 Envirostor ID: L10003156547 Other Ascertainable Records RCRA NonGen / NLR: RCRAInfo is EPA’s comprehensive information system, providing access to data supporting the Resource Conservation and Recovery Act (RCRA) of 1976 and the Hazardous and Solid Waste Amendments (HSWA) of 1984. The database includes selective information on sites which generate, transport, store, treat and/or dispose of hazardous waste as defined by the Resource Conservation and Recovery Act (RCRA). Non-Generators do not presently generate hazardous waste. A review of the RCRA NonGen / NLR list, as provided by EDR, and dated 09/13/2017 has revealed that there is 1 RCRA NonGen / NLR site within approximately 0.25 miles of the target property. PageMapIDDirection / DistanceAddressEqual/Higher Elevation ____________________ ________ ___________________ _____ _____ RAYCHEM CORP 1669 BRANDYWINE AVE E 1/8 - 1/4 (0.142 mi.) 12 45 CA BOND EXP. PLAN: Department of Health Services developed a site-specific expenditure plan as the basis for an appropriation of Hazardous Substance Cleanup Bond Act funds. It is not updated. A review of the CA BOND EXP. PLAN list, as provided by EDR, and dated 01/01/1989 has revealed that there are 2 CA BOND EXP. PLAN sites within approximately 1 mile of the target property. PageMapIDDirection / DistanceAddressLowerElevation ____________________ ________ ___________________ _____ _____ FORMER OMAR RENDERIN 1886 AUTO PARK PLACE E 1/4 - 1/2 (0.251 mi.) 21 76 APACHE SERVICES 4551 OTAY VALLEY ROA WSW 1/2 - 1 (0.765 mi.) 27 99 CA Cortese: The sites for the list are designated by the State Water Resource Control Board (LUST), the Integrated Waste Board (SWF/LS), and the Department of Toxic Substances Control (Cal-Sites). A review of the CA Cortese list, as provided by EDR, and dated 09/21/2017 has revealed that there is 1 CA Cortese site within approximately 0.5 miles of the target property. PageMapIDDirection / DistanceAddressLowerElevation ____________________ ________ ___________________ _____ _____ FORMER OMAR RENDERIN 1886 AUTO PARK PLACE E 1/4 - 1/2 (0.251 mi.) 21 76 EXECUTIVE SUMMARY TC5146125.2s EXECUTIVE SUMMARY 13 CA HIST CORTESE: The sites for the list are designated by the State Water Resource Control Board [LUST], the Integrated Waste Board [SWF/LS], and the Department of Toxic Substances Control [CALSITES]. This listing is no longer updated by the state agency. A review of the CA HIST CORTESE list, as provided by EDR, and dated 04/01/2001 has revealed that there is 1 CA HIST CORTESE site within approximately 0.5 miles of the target property. PageMapIDDirection / DistanceAddressLowerElevation ____________________ ________ ___________________ _____ _____ PACIFIC BELL 490 OTAY VALLEY RD SW 1/8 - 1/4 (0.145 mi.) E13 48 Reg Id: 9UT1584 CA HWP: Detailed information on permitted hazardous waste facilities and corrective action cleanups") tracked in EnviroStor. A review of the CA HWP list, as provided by EDR, and dated 08/21/2017 has revealed that there is 1 CA HWP site within approximately 1 mile of the target property. PageMapIDDirection / DistanceAddressEqual/Higher Elevation ____________________ ________ ___________________ _____ _____ ALLIED WASTE - OTAY 1700 MAXWELL ROAD ENE 1/2 - 1 (0.908 mi.) I29 101 EPA Id: CAT080010101 Cleanup Status: CLOSED EXECUTIVE SUMMARY TC5146125.2s EXECUTIVE SUMMARY 14 Due to poor or inadequate address information, the following sites were not mapped. Count: 5 records. Site Name Database(s)____________ ____________ OTAY MESA CID DRUMS SEMS SHINOHARA II CA SWF/LF WALKER SCOTT PROPERTY CA WMUDS/SWAT, CA San Diego Co. HMMD PUBLIC STORAGE FACILITY CA SAN DIEGO CO. SAM ARCO CA SAN DIEGO CO. SAM EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc. 60 kV 44400 240 440440440 240320 280240240 240 200 200160 160 320280240240 200 160 160 120 80 EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc. 240 MAP FINDINGS SUMMARY Search TargetDistance Total Database Property(Miles) < 1/8 1/8 - 1/4 1/4 - 1/2 1/2 - 1 > 1 Plotted STANDARD ENVIRONMENTAL RECORDS Federal NPL site list 0NR00001.000NPL 0NR00001.000ProposedNPL 0NRNRNRNRNRTPNPLLIENS Federal Delisted NPL site list 0NR00001.000DelistedNPL Federal CERCLIS list 0NRNR0000.500FEDERALFACILITY 0NRNR0000.500SEMS Federal CERCLIS NFRAP site list 1NRNR1000.500SEMS-ARCHIVE Federal RCRA CORRACTS facilities list 1NR10001.000CORRACTS Federal RCRA non-CORRACTS TSD facilities list 0NRNR0000.500RCRA-TSDF Federal RCRA generators list 1NRNRNR100.250RCRA-LQG 6NRNRNR600.250RCRA-SQG 1NRNRNR100.250RCRA-CESQG Federal institutional controls / engineering controls registries 0NRNR0000.500LUCIS 0NRNR0000.500USENGCONTROLS 0NRNR0000.500USINSTCONTROL Federal ERNS list 0NRNRNRNRNRTPERNS State- and tribal - equivalent NPL 0NR00001.000CARESPONSE State- and tribal - equivalent CERCLIS 4NR31001.000CAENVIROSTOR State and tribal landfill and/or solid waste disposal site lists 1NRNR1000.500CASWF/LF State and tribal leaking storage tank lists 2NRNR0200.500CASANDIEGOCO. SAM TC5146125.2s Page 4 MAP FINDINGS SUMMARY Search TargetDistance Total Database Property(Miles) < 1/8 1/8 - 1/4 1/4 - 1/2 1/2 - 1 > 1 Plotted 3NRNR1200.500CALUST 0NRNR0000.500INDIANLUST 2NRNR1010.500CASLIC State and tribal registered storage tank lists 0NRNRNR000.250FEMAUST 1NRNRNR100.250CAUST 3NRNRNR300.250CAAST 0NRNRNR000.250INDIANUST State and tribal voluntary cleanup sites 0NRNR0000.500CAVCP 0NRNR0000.500INDIANVCP State and tribal Brownfields sites 0NRNR0000.500CABROWNFIELDS ADDITIONAL ENVIRONMENTAL RECORDS Local Brownfield lists 1NRNR1000.500USBROWNFIELDS Local Lists of Landfill / Solid Waste Disposal Sites 1NRNR0010.500CAWMUDS/SWAT 0NRNR0000.500CASWRCY 0NRNRNRNRNRTPCAHAULERS 0NRNR0000.500INDIANODI 0NRNR0000.500DEBRISREGION9 0NRNR0000.500ODI 0NRNR0000.500IHSOPENDUMPS Local Lists of Hazardous waste / Contaminated Sites 0NRNRNRNRNRTPUSHISTCDL 0NR00001.000CAHISTCal-Sites 0NRNRNR000.250CASCH 0NRNRNRNRNRTPCACDL 0NRNRNRNRNRTPCASanDiegoCo. HMMD 0NR00001.000CAToxicPits 0NRNRNRNRNRTPUSCDL Local Lists of Registered Storage Tanks 3NRNRNR210.250CASWEEPSUST 2NRNRNR110.250CAHISTUST 0NRNRNR000.250CAFIDUST Local Land Records 0NRNRNRNRNRTPCALIENS 0NRNRNRNRNRTPLIENS2 TC5146125.2s Page 5 MAP FINDINGS SUMMARY Search TargetDistance Total Database Property(Miles) < 1/8 1/8 - 1/4 1/4 - 1/2 1/2 - 1 > 1 Plotted 1NRNR1000.500CADEED Records of Emergency Release Reports 0NRNRNRNRNRTPHMIRS 0NRNRNRNRNRTPCACHMIRS 0NRNRNRNRNRTPCALDS 0NRNRNRNRNRTPCAMCS 0NRNRNRNRNRTPCASPILLS90 Other Ascertainable Records 1NRNRNR100.250RCRANonGen / NLR 0NR00001.000FUDS 0NR00001.000DOD 0NRNR0000.500SCRDDRYCLEANERS 0NRNRNRNRNRTPUSFINASSUR 0NRNRNRNRNRTPEPAWATCHLIST 0NRNRNR000.2502020CORACTION 0NRNRNRNRNRTPTSCA 0NRNRNRNRNRTPTRIS 0NRNRNRNRNRTPSSTS 0NR00001.000ROD 0NRNRNRNRNRTPRMP 0NRNRNRNRNRTPRAATS 0NRNRNRNRNRTPPRP 0NRNRNRNRNRTPPADS 0NRNRNRNRNRTPICIS 0NRNRNRNRNRTPFTTS 0NRNRNRNRNRTPMLTS 0NRNRNRNRNRTPCOALASHDOE 0NRNR0000.500COALASHEPA 0NRNRNRNRNRTPPCBTRANSFORMER 0NRNRNRNRNRTPRADINFO 0NRNRNRNRNRTPHISTFTTS 0NRNRNRNRNRTPDOTOPS 0NR00001.000CONSENT 0NR00001.000INDIANRESERV 0NR00001.000FUSRAP 0NRNR0000.500UMTRA 0NRNRNRNRNRTPLEADSMELTERS 0NRNRNRNRNRTPUSAIRS 0NRNRNR000.250USMINES 0NRNRNR000.250ABANDONEDMINES 0NRNRNRNRNRTPFINDS 0NRNRNRNRNRTPDOCKETHWC 0NRNRNRNRNRTPECHO 0NR00001.000UXO 0NRNRNR000.250FUELSPROGRAM 2NR11001.000CABONDEXP. PLAN 1NRNR1000.500CACortese 0NRNRNR000.250CACUPAListings 0NRNRNR000.250CADRYCLEANERS TC5146125.2s Page 6 MAP FINDINGS SUMMARY Search TargetDistance Total Database Property(Miles) < 1/8 1/8 - 1/4 1/4 - 1/2 1/2 - 1 > 1 Plotted 0NRNRNRNRNRTPCAEMI 0NRNRNRNRNRTPCAENF 0NRNRNRNRNRTPCAFinancialAssurance 0NRNRNRNRNRTPCAHAZNET 0NRNRNRNRNRTPCAICE 1NRNR0100.500CAHISTCORTESE 1NR10001.000CAHWP 0NRNRNR000.250CAHWT 0NRNRNR000.250NYMANIFEST 0NRNRNR000.250CAMINES 0NRNRNR000.250CAMWMP 0NRNRNRNRNRTPCANPDES 0NRNRNRNRNRTPCAPESTLIC 0NRNR0000.500CAPROC 0NR00001.000CANotify65 0NRNRNRNRNRTPCAUIC 0NRNR0000.500CAWASTEWATERPITS 0NRNRNRNRNRTPCAWDS 0NRNRNR000.250CAWIP EDR HIGH RISK HISTORICAL RECORDS EDR Exclusive Records 0NR00001.000EDRMGP 0NRNRNRNR00.125EDRHistAuto 0NRNRNRNR00.125EDRHistCleaner EDR RECOVERED GOVERNMENT ARCHIVES Exclusive Recovered Govt. Archives 0NRNRNRNRNRTPCARGALF 0NRNRNRNRNRTPCARGALUST 400692140- Totals -- NOTES: TP = Target Property NR = Not Requested at this Search Distance Sites may be listed in more than one database TC5146125.2s Page 7 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedSelf-Monitoring Rept. Frequency: AWasteDischargeRequirements: NotreportedRCRAFacility: NotreportedSectionRange: 1NumberofWMUDSatFacility: BKMRegionalBoardProjectOfficer: TrueSubChapter15: NotreportedThreattoWaterQuality: NotreportedSolidWasteAssessmentTestProgram: FalseDepartmentofDefence: FalseResourceConservationRecoveryAct: FalseToxicPitsCleanupActProgram: FalseSolidWasteAssessmentTestProgram: TrueWasteDischargeSystem: NotreportedLastFacilityEditors: NotreportedComments: NotreportedSecondarySIC: 2869PrimarySIC: NotreportedSWATFacilityName: NotreportedFacilityTelephone: NotreportedFacilityDescription: Industrial, Agricultural or Solid Waste (Class I, II or III) Other - Does not fall into the category of Municipal/Domestic,Facility Type: 9Region: NotreportedLandOwnerPhone: NotreportedLandOwnerContact: NotreportedLandOwnerCity,St,Zip: NotreportedLandOwnerAddress: NotreportedLandOwnerName: 6194580943AgencyTelephone: DONBARRIGAgencyContact: LOS ANGELES CA90017AgencyCity,St,Zip: 725 SFIGUEROAAgencyAddress: NotreportedAgencyDepartment: CHULA VISTA INDUSTRIALREALTYAgencyName: StateAgencyType: FalseWasteList: FalseOpenToPublic: FalseSuperorder: FalseMunicipalSolidWaste: NotreportedRegionalBoardID: 0Tonnage: NotreportedNPID: NotreportedBaseMeridian: NotreportedSecondaryWasteType: NotreportedSecondaryWaste: applicable DOHS standards. ignitable or reactive substances and must be managed according to Hazardous/Influent or Solid Wastes that contain toxic, corrosive,Primary Waste Type: PROCESPrimaryWaste: NotreportedComplexity: NotreportedEditDate: WMUDS/SWAT: 92 ft. Site 1 of 2 in cluster A 0.017 mi. Relative: Lower Actual: 165 ft. 1/8 CHULA VISTA CA, CA 91911 ESE 1670 & 1690 BRANDYWINE AVE N/A A1 CA WMUDS/SWATBRANDYWINEDISTRIBUTIONCENTER S103443331 TC5146125.2s Page 8 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedSolidWasteInformationID: 9000247N96WasteDischargeSystemID: BRANDYWINE DISTRIBUTION CENTER (Continued) S103443331 Click here to access the California GeoTracker records for this facility: closed. appears to not be a source of pollution this case is administratively that potential threat exists twenty years later. Since this property Collection of more recent ground-water data would help to verify if samples collected in 1996, suggests a potential threat to indoor air. gradient of this location. Using today’s standards, ground-water the Former Omar Rendering site immediately to the east and up were not the source of these pollutants and that the likely source is provided, historical operations/activities conducted at this location compounds (e.g. trichloroethylene). Based on the information water has been impacted by pollutants, primarily volatile organic impacted by pollutants originating from the property and that ground May 1996 concluded that the soil beneath this location has not been Recent review of the Soil & Ground- water Investigation ReportdatedSiteHistory: Xylene Copper, Lead, Mercury (elemental), Nickel, Other Metal, Zinc, Benzene, Tetrachloroethylene (PCE), Trichloroethylene (TCE), Arsenic, Chromium, Dichloroethene (DCE), Other Chlorinated Hydrocarbons,Potential Contaminants of Concern: Indoor Air, Other Groundwater (uses other than drinking water)Potential Media Affected: RegionalBoardFileLocation: 9000247N96RBCaseNumber: NotreportedLocalAgency: UNACaseWorker: Cleanup ProgramSiteCaseType: 117.029746770859Longitude: 32.5964775432941Latitude: NotreportedLeadAgencyCaseNumber: SAN DIEGO RWQCB (REGION 9)Lead Agency: L10003764847GlobalId: 05/03/2017StatusDate: Completed - CaseClosedFacilityStatus: STATERegion: SLIC: 261 ft. Site 2 of 2 in cluster A 0.049 mi. Relative: Lower Actual: 156 ft. 1/8 CHULA VISTA, CA 91911 ESE 1670 & 1690 BRANDYWINE AVE N/A A2 CASLICBRANDYWINEDISTRIBUTIONCENTER S120762563 44-023037BoardOfEqualization: 9Number: 19570CompNumber: ActiveStatus: SWEEPS UST: 573 ft. Site 1 of 2 in cluster B 0.109 mi. Relative: Lower Actual: 146 ft. 1/8 CHULA VISTA, CA 91911 SE 1685 BRANDYWINE AVE N/A B3 CA SWEEPSUSTHYSPANPRECISIONPRODUCTSINC S102862245 TC5146125.2s Page 9 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 1NumberOfTanks: OTHERContent: PSTG: M.V. FUELTankUse: NotreportedActiveDate: 1000Capacity: ATankStatus: 37-000-019570-000001SWRCBTankId: NotreportedOwnerTankId: 02-29-88CreatedDate: 06-26-92ActionDate: NotreportedReferralDate: HYSPAN PRECISION PRODUCTS INC (Continued) S102862245 Click here for Geo Tracker PDF: VisualLeakDetection: NotreportedContainerConstructionThickness: DIESELTypeofFuel: PRODUCTTankUsedfor: 00001000TankCapacity: 1983YearInstalled: 001ContainerNum: 001TankNum: 0001TotalTanks: SAN DIEGO, CA92106OwnerCity,St,Zip: 3028MCCALLOwnerAddress: DONALD R. HEYEOwnerName: 6194211355Telephone: WILLIAM T. AUSTIN, FACILITIESContactName: MANUFACTURINGOtherType: OtherFacilityType: 00000002098FacilityID: STATERegion: http://geotracker.waterboards.ca.gov/ustpdfs/pdf/0002B114.pdfURL: 0002B114FileNumber: HIST UST: 573 ft. Site 2 of 2 in cluster B 0.109 mi. Relative: Lower Actual: 146 ft. 1/8 CHULA VISTA, CA 92011 SE 1685 BRANDYWINE AVE N/A B4 CA HISTUSTHYSPANPRECISIONPRODUCTSINC 1000345124 CAD080922529EPAID: CHULA VISTA, CA 91911 516 TALLOWCTFacilityaddress: JO-BIE PRODUCTSCOMPANYFacilityname: 09/01/1996Dateformreceivedbyagency: RCRA-SQG: 697 ft. 0.132 mi. Relative: Higher Actual: 226 ft. 1/8-1/4 ECHOCHULAVISTA, CA 91911 NNW FINDS516TALLOWCT CAD080922529 5 RCRA-SQGJO-BIE PRODUCTS COMPANY 1000163373 TC5146125.2s Page 10 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NoUsedoiltransferfacility: NoUsedoilSpecificationmarketer: NoUsedoilfuelmarketertoburner: NoUseroilrefiner: NoUsedoilprocessor: NoUsedoilfuelburner: NoFurnaceexemption: NoOn-site burner exemption: NoUndergroundinjectionactivity: NoTreater, storer or disposer of HW: NoTransporterofhazardouswaste: NoRecyclerofhazardouswaste: NoMixedwaste (haz. and radioactive): NoU.S. importer of hazardous waste: Handler Activities Summary: NotreportedOwner/Op end date: NotreportedOwner/Op start date: OperatorOwner/Operator Type: PrivateLegalstatus: NotreportedOwner/operator extension: NotreportedOwner/operator fax: NotreportedOwner/operator email: 415-555-1212Owner/operator telephone: NotreportedOwner/operator country: NOT REQUIRED, ME 99999 NOTREQUIREDOwner/operator address: NOTREQUIREDOwner/operator name: NotreportedOwner/Op end date: NotreportedOwner/Op start date: OwnerOwner/Operator Type: PrivateLegalstatus: NotreportedOwner/operator extension: NotreportedOwner/operator fax: NotreportedOwner/operator email: 415-555-1212Owner/operator telephone: NotreportedOwner/operator country: NOT REQUIRED, ME 99999 NOTREQUIREDOwner/operator address: JOSEPH&EDUVIJESHAVERLANDOwner/operator name: Owner/Operator Summary: hazardous waste at any time waste during any calendar month, and accumulates more than 1000 kg of hazardous waste at any time; or generates 100 kg or less of hazardous waste during any calendar month and accumulates less than 6000 kg of Handler: generates more than 100 and less than 1000 kg ofhazardousDescription: Small Small QuantityGeneratorClassification: 09EPARegion: NotreportedContactemail: NotreportedContacttelephone: USContactcountry: Not reported NotreportedContactaddress: NotreportedContact: JO-BIE PRODUCTS COMPANY (Continued) 1000163373 TC5146125.2s Page 11 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation http://echo.epa.gov/detailed-facility-report?fid=110006467867DFRURL: 110006467867RegistryID: 1000163373Envid: ECHO: additional FINDS: detail in the EDR Site Report. Click this hyperlink while viewing on your computer to access corrective action activities required under RCRA. program staff to track the notification, permit, compliance, and and treat, store, or dispose of hazardous waste. RCRAInfo allows RCRA events and activities related to facilities that generate, transport, Conservation and Recovery Act (RCRA) program through the tracking of RCRAInfo is a national information system that supports the Resource Environmental Interest/Information System 110006467867RegistryID: FINDS: No violationsfoundViolationStatus: Large QuantityGeneratorClassification: JO-BIE PRODUCTSCOMPANYSitename: 08/05/1980Dateformreceivedbyagency: Historical Generators: NoUsedoiltransporter: JO-BIE PRODUCTS COMPANY (Continued) 1000163373 cleanup of a spill, into or on any land or water, of acutely hazardous residue or contaminated soil, waste or other debris resulting from the during any calendar month; or generates more than 100 kg of any calendar month; or generates more than 1 kg of acutely hazardous waste Handler: generates 1,000 kg or more of hazardous waste duringanyDescription: Large QuantityGeneratorClassification: PrivateLandtype: 09EPARegion: TIMOTHY_J_HILL@DRESSER-RANDContactemail: 619-656-4740Contacttelephone: USContactcountry: Not reported NotreportedContactaddress: TIMOTHY JHILLContact: CAR000150854EPAID: CHULA VISTA, CA 91911 SUITE F 1675 BRANDYWINEAVENUEFacilityaddress: DRESSER-RAND REAPIRCENTERFacilityname: 01/25/2006Dateformreceivedbyagency: RCRA-LQG: 706 ft. Site 1 of 3 in cluster C 0.134 mi. Relative: Lower Actual: 154 ft. 1/8-1/4 CHULA VISTA, CA 91911 ESE 1675 BRANDYWINE AVENUE CAR000150854 C6 RCRA-LQGDRESSER-RAND REAPIR CENTER 1007200720 TC5146125.2s Page 12 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation PrivateLegalstatus: NotreportedOwner/operator extension: NotreportedOwner/operator fax: NotreportedOwner/operator email: NotreportedOwner/operator telephone: USOwner/operator country: OLEAN, NY 14760 PAUL CLARKDRIVEOwner/operator address: DRESSER-RANDOwner/operator name: NotreportedOwner/Op end date: 01/01/2003Owner/Op start date: OperatorOwner/Operator Type: PrivateLegalstatus: NotreportedOwner/operator extension: NotreportedOwner/operator fax: NotreportedOwner/operator email: NotreportedOwner/operator telephone: USOwner/operator country: Not reported NotreportedOwner/operator address: DRESSER-RANDOwner/operator name: NotreportedOwner/Op end date: 01/01/2004Owner/Op start date: OwnerOwner/Operator Type: PrivateLegalstatus: NotreportedOwner/operator extension: NotreportedOwner/operator fax: NotreportedOwner/operator email: NotreportedOwner/operator telephone: USOwner/operator country: Not reported NotreportedOwner/operator address: YALECOOwner/operator name: NotreportedOwner/Op end date: 01/01/2004Owner/Op start date: OperatorOwner/Operator Type: PrivateLegalstatus: NotreportedOwner/operator extension: NotreportedOwner/operator fax: NotreportedOwner/operator email: NotreportedOwner/operator telephone: USOwner/operator country: Not reported NotreportedOwner/operator address: DRESSER RANDCOOwner/operator name: Owner/Operator Summary: 100 kg of that material at any time hazardous waste during any calendar month, and accumulates more than from the cleanup of a spill, into or on any land or water, of acutely of any residue or contaminated soil, waste or other debris resulting kg of acutely hazardous waste at any time; or generates 100 kg or less hazardous waste during any calendar month, and accumulates more than 1 waste during any calendar month; or generates 1 kg or less of acutely DRESSER-RAND REAPIR CENTER (Continued) 1007200720 TC5146125.2s Page 13 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation D018. Waste code: LEAD. Waste name: D008. Waste code: CHROMIUM. Waste name: D007. Waste code: CADMIUM. Waste name: D006. Waste code: CORROSIVE WASTE. Waste name: D002. Waste code: IGNITABLE WASTE. Waste name: D001. Waste code: Liquids with halogenated organic compounds > 1000 mg/l. Waste name: 741. Waste code: Other organic solids. Waste name: 352. Waste code: Organic liquids with metals (see 121). Waste name: 342. Waste code: Oxygenated solvents (acetone, butanol, ethyl acetate, etc.). Waste name: 212. Waste code: Other inorganic solid waste. Waste name: 181. Waste code: molybdenum, nickel, selenium, silver, thallium, vanadium, and zinc) beryllium, cadmium, chromium, cobalt, copper, lead, mercury, Alkaline solution (pH >12.5) with metals (antimony, arsenic, barium,. Waste name: 121. Waste code: NoUsedoiltransporter: NoUsedoiltransferfacility: NoUsedoilSpecificationmarketer: NoUsedoilfuelmarketertoburner: NoUseroilrefiner: NoUsedoilprocessor: NoUsedoilfuelburner: NoFurnaceexemption: NoOn-site burner exemption: NoUndergroundinjectionactivity: NoTreater, storer or disposer of HW: NoTransporterofhazardouswaste: NoRecyclerofhazardouswaste: NoMixedwaste (haz. and radioactive): NoU.S. importer of hazardous waste: Handler Activities Summary: NotreportedOwner/Op end date: 01/01/2003Owner/Op start date: OwnerOwner/Operator Type: DRESSER-RAND REAPIR CENTER (Continued) 1007200720 TC5146125.2s Page 14 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation Small QuantityGeneratorClassification: DRESSER RANDCOMPANYSitename: 02/09/2004Dateformreceivedbyagency: Historical Generators: THESE SPENT SOLVENTS AND SPENT SOLVENT MIXTURES. LISTED IN F001, F002, OR F004; AND STILL BOTTOMS FROM THE RECOVERY OF ONE OR MORE OF THE ABOVE NONHALOGENATED SOLVENTS OR THOSE SOLVENTS CONTAINING, BEFORE USE, A TOTAL OF TEN PERCENT OR MORE (BY VOLUME) OF 2-ETHOXYETHANOL, AND 2-NITROPROPANE; ALL SPENT SOLVENT MIXTURES/BLENDS KETONE, CARBON DISULFIDE, ISOBUTANOL, PYRIDINE, BENZENE, THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: TOLUENE, METHYL ETHYL. Waste name: F005. Waste code: MIXTURES. BOTTOMS FROM THE RECOVERY OF THESE SPENT SOLVENTS AND SPENT SOLVENT MORE OF THOSE SOLVENTS LISTED IN F001, F002, F004, AND F005; AND STILL SOLVENTS, AND A TOTAL OF TEN PERCENT OR MORE (BY VOLUME) OF ONE OR CONTAINING, BEFORE USE, ONE OR MORE OF THE ABOVE NONHALOGENATED NONHALOGENATED SOLVENTS; AND ALL SPENT SOLVENT MIXTURES/BLENDS MIXTURES/BLENDS CONTAINING, BEFORE USE, ONLY THE ABOVE SPENT ALCOHOL, CYCLOHEXANONE, AND METHANOL; ALL SPENT SOLVENT ACETATE, ETHYL BENZENE, ETHYL ETHER, METHYL ISOBUTYL KETONE, N-BUTYL THE FOLLOWING SPENT NONHALOGENATED SOLVENTS: XYLENE, ACETONE, ETHYL. Waste name: F003. Waste code: SPENT SOLVENT MIXTURES. F005; AND STILL BOTTOMS FROM THE RECOVERY OF THESE SPENT SOLVENTS AND ABOVE HALOGENATED SOLVENTS OR THOSE SOLVENTS LISTED IN F001, F004, AND USE, A TOTAL OF TEN PERCENT OR MORE (BY VOLUME) OF ONE OR MORE OF THE TRICHLOROETHANE; ALL SPENT SOLVENT MIXTURES/BLENDS CONTAINING, BEFORE ORTHO-DICHLOROBENZENE, TRICHLOROFLUOROMETHANE, AND 1,1,2, CHLOROBENZENE, 1,1,2-TRICHLORO-1,2,2-TRIFLUOROETHANE, METHYLENE CHLORIDE, TRICHLOROETHYLENE, 1,1,1-TRICHLOROETHANE, THE FOLLOWING SPENT HALOGENATED SOLVENTS: TETRACHLOROETHYLENE,. Waste name: F002. Waste code: TRICHLORETHYLENE. Waste name: D040. Waste code: TETRACHLOROETHYLENE. Waste name: D039. Waste code: PYRIDINE. Waste name: D038. Waste code: NITROBENZENE. Waste name: D036. Waste code: METHYL ETHYL KETONE. Waste name: D035. Waste code: 1,4-DICHLOROBENZENE. Waste name: D027. Waste code: BENZENE. Waste name: DRESSER-RAND REAPIR CENTER (Continued) 1007200720 TC5146125.2s Page 15 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 02/01/2006Dateachievedcompliance: Generators - GeneralAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 01/11/2006Evaluationdate: StateEvaluationleadagency: NotreportedDateachievedcompliance: NotreportedAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 11/06/2007Evaluationdate: Evaluation Action Summary: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 01/11/2006Enforcementactiondate: WRITTEN INFORMALEnforcementaction: StateViolationleadagency: 02/01/2006Dateachievedcompliance: 01/11/2006Dateviolationdetermined: Generators - GeneralAreaofviolation: NotreportedRegulationviolated: Facility Has Received Notices of Violations: SILVER. Waste name: D011. Waste code: SELENIUM. Waste name: D010. Waste code: MERCURY. Waste name: D009. Waste code: LEAD. Waste name: D008. Waste code: CHROMIUM. Waste name: D007. Waste code: CADMIUM. Waste name: D006. Waste code: BARIUM. Waste name: D005. Waste code: ARSENIC. Waste name: D004. Waste code: CORROSIVE WASTE. Waste name: D002. Waste code: IGNITABLE WASTE. Waste name: D001. Waste code: DRESSER-RAND REAPIR CENTER (Continued) 1007200720 TC5146125.2s Page 16 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation LocalEvaluationleadagency: DRESSER-RAND REAPIR CENTER (Continued) 1007200720 NoUsedoilSpecificationmarketer: NoUsedoilfuelmarketertoburner: NoUseroilrefiner: NoUsedoilprocessor: NoUsedoilfuelburner: NoFurnaceexemption: NoOn-site burner exemption: NoUndergroundinjectionactivity: NoTreater, storer or disposer of HW: NoTransporterofhazardouswaste: NoRecyclerofhazardouswaste: NoMixedwaste (haz. and radioactive): NoU.S. importer of hazardous waste: Handler Activities Summary: NotreportedOwner/Op end date: NotreportedOwner/Op start date: OwnerOwner/Operator Type: PrivateLegalstatus: NotreportedOwner/operator extension: NotreportedOwner/operator fax: NotreportedOwner/operator email: 503-655-8940Owner/operator telephone: NotreportedOwner/operator country: CLACKAMAS, OR 97015 16277 SE 130THAVEOwner/operator address: CODE A PHONECORPOwner/operator name: Owner/Operator Summary: hazardous waste at any time waste during any calendar month, and accumulates more than 1000 kg of hazardous waste at any time; or generates 100 kg or less of hazardous waste during any calendar month and accumulates less than 6000 kg of Handler: generates more than 100 and less than 1000 kg ofhazardousDescription: Small Small QuantityGeneratorClassification: 09EPARegion: NotreportedContactemail: 619-421-7937Contacttelephone: USContactcountry: CHULA VISTA, CA 91911-8944 1675 BRANDYWINE AVE STEBContactaddress: BASILDIXONContact: CHULA VISTA, CA 91911-8944 BRANDYWINE AVE STEBMailingaddress: CA0001000991EPAID: CHULA VISTA, CA 91911-8944 1675 BRANDYWINE AVE STEBFacilityaddress: CODE A PHONECORPFacilityname: 01/06/1995Dateformreceivedbyagency: RCRA-SQG: 706 ft. Site 2 of 3 in cluster C 0.134 mi.CA HAZNET Relative: Lower Actual: 154 ft. 1/8-1/4 ECHOCHULAVISTA, CA 91911 ESE FINDS1675BRANDYWINEAVESTEB CA0001000991 C7 RCRA-SQGCODEAPHONECORP 1000978278 TC5146125.2s Page 17 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation SanDiegoFacilityCounty: NotreportedMethodDecode: NotreportedCatDecode: 1.5428Tons: TransferStationDisposalMethod: Other inorganic solidwasteWasteCategory: NotreportedTSDCounty: CAD088504881TSDEPAID: NotreportedGenCounty: CHULA VISTA, CA919110000MailingCity,St,Zip: 1675 BRANDYWINE AVE STEBMailingAddress: NotreportedMailingName: 6194217937Telephone: CODE A PHONECORPContact: CA0001000991GEPAID: 1995Year: 1000978278envid: HAZNET: http://echo.epa.gov/detailed-facility-report?fid=110002622350DFRURL: 110002622350RegistryID: 1000978278Envid: ECHO: additional FINDS: detail in the EDR Site Report. Click this hyperlink while viewing on your computer to access corrective action activities required under RCRA. program staff to track the notification, permit, compliance, and and treat, store, or dispose of hazardous waste. RCRAInfo allows RCRA events and activities related to facilities that generate, transport, Conservation and Recovery Act (RCRA) program through the tracking of RCRAInfo is a national information system that supports the Resource Environmental Interest/Information System 110002622350RegistryID: FINDS: No violationsfoundViolationStatus: NoUsedoiltransporter: NoUsedoiltransferfacility: CODE A PHONE CORP (Continued)1000978278 CAR000099267EPAID: CHULA VISTA, CA 91911 1675 BRANDYWINE STEAFacilityaddress: ANTEONCORPORATIONFacilityname: 07/02/2001Dateformreceivedbyagency: RCRA-CESQG: 706 ft. Site 3 of 3 in cluster C 0.134 mi. Relative: Lower Actual: 154 ft. 1/8-1/4 ECHOCHULAVISTA, CA 91911 ESE FINDS1675BRANDYWINESTEA CAR000099267 C8 RCRA-CESQGANTEONCORPORATION 1004677590 TC5146125.2s Page 18 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation IGNITABLE WASTE. Waste name: D001. Waste code: NoUsedoiltransporter: NoUsedoiltransferfacility: NoUsedoilSpecificationmarketer: NoUsedoilfuelmarketertoburner: NoUseroilrefiner: NoUsedoilprocessor: NoUsedoilfuelburner: NoFurnaceexemption: NoOn-site burner exemption: NoUndergroundinjectionactivity: NoTreater, storer or disposer of HW: YesTransporterofhazardouswaste: NoRecyclerofhazardouswaste: NoMixedwaste (haz. and radioactive): NoU.S. importer of hazardous waste: Handler Activities Summary: NotreportedOwner/Op end date: NotreportedOwner/Op start date: OwnerOwner/Operator Type: PrivateLegalstatus: NotreportedOwner/operator extension: NotreportedOwner/operator fax: NotreportedOwner/operator email: 703-246-0200Owner/operator telephone: NotreportedOwner/operator country: FAIRFAX, VA 22030 3211 JERMANTOWN RD STE200Owner/operator address: ANTEONCORPOwner/operator name: Owner/Operator Summary: hazardous waste the cleanup of a spill, into or on any land or water, of acutely any residue or contaminated soil, waste or other debris resulting from time: 1 kg or less of acutely hazardous waste; or 100 kg or less of hazardous waste during any calendar month, and accumulates at any from the cleanup of a spill, into or on any land or water, of acutely of any residue or contaminated soil, waste or other debris resulting land or water, of acutely hazardous waste; or generates 100 kg or less other debris resulting from the cleanup of a spill, into or on any waste; or 100 kg or less of any residue or contaminated soil, waste or month, and accumulates at any time: 1 kg or less of acutely hazardous or generates 1 kg or less of acutely hazardous waste per calendar month, and accumulates 1000 kg or less of hazardous waste at any time; Handler: generates 100 kg or less of hazardous waste percalendarDescription: Conditionally Exempt Small QuantityGeneratorClassification: 09EPARegion: NotreportedContactemail: 619-881-8918Contacttelephone: USContactcountry: CHULA VISTA, CA 91911 1675 BRANDYWINE STEAContactaddress: VELDASMITHContact: ANTEON CORPORATION (Continued) 1004677590 TC5146125.2s Page 19 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation http://echo.epa.gov/detailed-facility-report?fid=110012202892DFRURL: 110012202892RegistryID: 1004677590Envid: ECHO: additional FINDS: detail in the EDR Site Report. Click this hyperlink while viewing on your computer to access corrective action activities required under RCRA. program staff to track the notification, permit, compliance, and and treat, store, or dispose of hazardous waste. RCRAInfo allows RCRA events and activities related to facilities that generate, transport, Conservation and Recovery Act (RCRA) program through the tracking of RCRAInfo is a national information system that supports the Resource facilities. generators, transporters, and treatment, storage, and disposal provides California with information on hazardous waste shipments for California Hazardous Waste Tracking System - Datamart (HWTS-DATAMART) Environmental Interest/Information System 110012202892RegistryID: FINDS: No violationsfoundViolationStatus: ANTEON CORPORATION (Continued) 1004677590 NotreportedPropertyOwnerCity: NotreportedPropertyOwnerMailingAddress: NotreportedPropertyOwnerPhone: NotreportedPropertyOwnerName: NotreportedOwnerCountry: NotreportedOwnerZipCode: NotreportedOwnerState: NotreportedOwnerMailAddress: NotreportedOwnerPhone: NotreportedOperatorPhone: NotreportedOperatorName: NotreportedMailingAddressZipCode: NotreportedMailingAddressState: NotreportedMailingAddressCity: NotreportedMailingAddress: NotreportedFax: NotreportedPhone: NotreportedBusinessName: NotreportedFacilityID: NotreportedCERSID: 2975TotalGallons: DOUGLASFULLEROwner: SanDiegoCertifiedUnifiedProgramAgencies: AST: 727 ft. Site 1 of 3 in cluster D 0.138 mi. Relative: Lower Actual: 130 ft. 1/8-1/4 CHULA VISTA, CA South 540/560 AUTO PARK DR N/A D9 CAASTFULLERFORD/HONDA A100345769 TC5146125.2s Page 20 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedEPAID: NotreportedPropertyOwnerCountry: NotreportedPropertyOwnerZipCode: NotreportedPropertyOwnerStat : FULLER FORD/HONDA (Continued)A100345769 YHandleRegulatedHazmat: NotreportedUSTOwner: 91911FacilityMailingZip: CAFacilityMailingState: CHULAVISTAFacilityMailingCity: 560 AUTO PARKDRFacilityMailingAddress: DOUGLASFULLERFacilityOwner: 11/02/2012DateLastUpdated: 06/30/2013PermitExpiration: OPENPermitStatus: 619-656-2500FacilityTelephone: 07/13/2010LastHMMDInspection: 644-042-04-00APN: CAR000003897EPAIdNumber: 6HK31BusinessType: 134845PermitNumber: HMMD SAN DIEGO: CAR000003897EPAID: UnitedStatesPropertyOwnerCountry: 91911PropertyOwnerZipCode: CAPropertyOwnerStat : CHULAVISTAPropertyOwnerCity: 560 AUTO PARKDRPropertyOwnerMailingAddress: NotreportedPropertyOwnerPhone: D G F FAMILY LTDPARTNERSHIPPropertyOwnerName: UnitedStatesOwnerCountry: 91911OwnerZipCode: CAOwnerState: 560 AUTO PARKDROwnerMailAddress: 619-656-2500OwnerPhone: 619-656-2500OperatorPhone: MartyMeadorOperatorName: 91911MailingAddressZipCode: CAMailingAddressState: CHULAVISTAMailingAddressCity: 560 AUTO PARKDRMailingAddress: NotreportedFax: 619-656-2500Phone: FULLER FORD/KIABusinessName: 37-000-134845FacilityID: 10358875CERSID: NotreportedTotalGallons: DouglasFullerOwner: NotreportedCertifiedUnifiedProgramAgencies: AST: 727 ft. Site 2 of 3 in cluster D 0.138 mi. Relative: Lower Actual: 130 ft. 1/8-1/4 CHULA VISTA, CA 91911 South CA San Diego Co. HMMD540AUTOPARKDR N/A D10 CAASTFULLERFORD/KIA S106064374 TC5146125.2s Page 21 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation WasteMaterialWaste: PARTS CLEANER CLEANINGSOLUTIONOtherInformation: WASTE 133 AQUEOUS SOL’N W/ 10% ORGRESIDName: NotreportedCaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: FIREHazardousCategories1: MaterialMaterialWaste: NotreportedOtherInformation: SOAP-DETAIL CHEMICALS/CASTROLName: MIXTURECaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: PRESSURERELEASEHazardousCategories2: FIREHazardousCategories1: MaterialMaterialWaste: NotreportedOtherInformation: PROPANEName: 68476-85-7CaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: FIREHazardousCategories1: MaterialMaterialWaste: NotreportedOtherInformation: LUBRICATING FLUID (BASE LUBRICATING OIL)Name: 647426-65-0CaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: ACUTEHazardousCategories1: MaterialMaterialWaste: NotreportedOtherInformation: LIQUID CAR WASH CONCENTRATE P-181FName: MIXTURECaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: ACUTEHazardousCategories2: PRESSURERELEASEHazardousCategories1: MaterialMaterialWaste: NotreportedOtherInformation: HELIUMName: 7740-59-7CaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: Inventory Active Permits (not SQG Medical): NotreportedGenerateMedicalWaste: NotreportedTreatHazWaste: YGenerateHazWaste: YSubjectToAPSA: NotreportedOwnOrOperateUST: FULLER FORD/KIA (Continued)S106064374 TC5146125.2s Page 22 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: USED ETHYLENE GLYCOL/COOLANTOtherInformation: WASTE 342 ORGANIC LIQUIDS W/METALSName: NotreportedCaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: OILY RAGS/SATURATEDABSORBENTSOtherInformation: WASTE 223 UNSPEC OIL CONTAININGWASTEName: NotreportedCaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: SLUDGE (OIL&WATER)Other Information: WASTE 222 OIL/WATER SEPARATIONSLUDGEName: NotreportedCaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: USEDOILOtherInformation: WASTE 221 WASTE OIL & MIXEDOILName: NotreportedCaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: WASTEGASOLINEOtherInformation: WASTE 214 UNSPEC SOLVENTMIXTUREName: NotreportedCaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: BRAKEWASHEROtherInformation: WASTE 214 UNSPEC SOLVENTMIXTUREName: NotreportedCaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: FULLER FORD/KIA (Continued)S106064374 TC5146125.2s Page 23 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 04/03/2007InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: 66262.34(f) Failed to properly label/date hazardous waste container &/or tank.Violation Citation: HAZWASTE TANK/CONTAINER W/O LABEL/DATEViolation: 6HV0227ViolationCode: 04/03/2007InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: from a container. 66261.7 (b), (d) &/or ( r) Failed to properly manage non-empty container or inner linerremovedViolationCitation: MISMANAGED NON-EMPTY CONTAINER/LINERViolation: 6HV0223ViolationCode: 04/03/2007InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: are now declared hazardous waste. HSC 25124(b)(3)(A) & 66262.34(f) Hazardous materials have not been adequately labeled within 10 days &Violation Citation: HAZMATS WITHOUT PROPERLABELSViolation: 6HV0216ViolationCode: 04/03/2007InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: Did not have adequate employee training program 2732 &/or 25504( c)Violation Citation: EMPLOYEE TRAINING NOTADEQUATEViolation: 6HV1015ViolationCode: 04/03/2007InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: Violations Active Permits: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: CRUSHEDOtherInformation: WASTE 888 USED OILFILTERSName: NotreportedCaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: NotreportedOtherInformation: WASTE 444 USEDBATTERIESName: NotreportedCaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: FULLER FORD/KIA (Continued)S106064374 TC5146125.2s Page 24 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 66262.34(a)(3) & 66262.34(f) date and/or are improperly labeled. CCR 66262.34(a)(2); Hazardous waste containers &/or tanks are missing labels, accumulationViolationCitation: WASTE CONTAINER W/OLABELSViolation: 6HV0202ViolationCode: 01/12/2004InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: 66265.173(a) Hazardous waste containers are not kept closed while in storage. CCRViolationCitation: WASTE CONTAINER NOTCLOSEDViolation: 6HV0201ViolationCode: 01/12/2004InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: 66265.195 ( c) Failed to inspect and/or document daily HW tank system inspections. Violation Citation: NO DAILY TANK INSPECTION/LOGViolation: 6HV1605ViolationCode: 04/03/2007InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: 66265.191(a) or 66265.192(a) Failed to obtain a P.E. assessment for hazardous waste tank system.Violation Citation: HAZWASTE TANKS W/O P.E. ASSESSMENTViolation: 6HV1601ViolationCode: 04/03/2007InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: waste is inadequate. CFR 262.34(d)(5)(iii) Employee training program for small quantity generator ofhazardousViolationCitation: EMPLOYEE TRAINING NOTADEQUATEViolation: 6HV0407ViolationCode: 04/03/2007InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: Waste accumulated in a container in poor condition. CFR 265.171ViolationCitation: HW CONTAINER IN POORCONDITIONViolation: 6HV0232ViolationCode: 04/03/2007InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: Failed to keep container closed. CFR 265.173ViolationCitation: CONTAINER NOT KEPTCLOSEDViolation: 6HV0228ViolationCode: FULLER FORD/KIA (Continued)S106064374 TC5146125.2s Page 25 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation ACTIVEActivity: 66265.191(a) or 66265.192(a) Failed to obtain a P.E. assessment for hazardous waste tank system.Violation Citation: HAZWASTE TANKS W/O P.E. ASSESSMENTViolation: 6HV1601ViolationCode: 09/08/2005InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: waste regulations. CCR 66265.16(a)&(b) Personnel training is not adequate to ensure compliance withhazardousViolationCitation: TRAINING PROGRAM NOTADEQUATEViolation: 6HV0402ViolationCode: 09/08/2005InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: 66262.34(a)&( c) without a State permit or written variance. CCR 25201(a) & Hazardous waste is stored in excess of allowable time period (90 days)Violation Citation: WASTE ONSITE >90/180/270DAYSViolation: 6HV0209ViolationCode: 09/08/2005InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: 66265.191(a) or 66265.192(a) Failed to obtain a P.E. assessment for hazardous waste tank system.Violation Citation: HAZWASTE TANKS W/O P.E. ASSESSMENTViolation: 6HV1601ViolationCode: 01/12/2004InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: 66265.16(d)&(e) with requirements for current and former employees. CCR Personnel training records are not maintained to documentcomplianceViolationCitation: TRAINING RECORDSUNAVAILABLEViolation: 6HV0401ViolationCode: 01/12/2004InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: explosion or release. CCR 66265.31 Facility not maintained &/operated to minimize possibility of fire,Violation Citation: FIRE/EXPLOSION/RELEASE NOTMINIMIZEDViolation: 6HV0207ViolationCode: 01/12/2004InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: FULLER FORD/KIA (Continued)S106064374 TC5146125.2s Page 26 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation FIREHazardousCategories1: MaterialMaterialWaste: NotreportedOtherInformation: LUBRICATING FLUID (BASE LUBRICATING OIL)Name: 647426-65-0CaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: ACUTEHazardousCategories1: MaterialMaterialWaste: NotreportedOtherInformation: LIQUID CAR WASH CONCENTRATE P-181FName: MIXTURECaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: ACUTEHazardousCategories2: PRESSURERELEASEHazardousCategories1: MaterialMaterialWaste: NotreportedOtherInformation: HELIUMName: 7740-59-7CaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: Inventory Active Permits (not SQG Medical): NotreportedGenerateMedicalWaste: NotreportedTreatHazWaste: YGenerateHazWaste: NotreportedSubjectToAPSA: NotreportedOwnOrOperateUST: YHandleRegulatedHazmat: NotreportedUSTOwner: 91911FacilityMailingZip: CAFacilityMailingState: CHULAVISTAFacilityMailingCity: 560 AUTO PARKDRFacilityMailingAddress: DOUGLASFULLERFacilityOwner: 11/02/2012DateLastUpdated: 06/30/2013PermitExpiration: OPENPermitStatus: 619-656-2500FacilityTelephone: 07/13/2010LastHMMDInspection: 644-042-04-00APN: CAR000003897EPAIdNumber: 6HK31BusinessType: 134845PermitNumber: ACTIVEActivity: 66265.195 ( c) Failed to inspect and/or document daily HW tank system inspections. Violation Citation: NO DAILY TANK INSPECTION/LOGViolation: 6HV1605ViolationCode: 09/08/2005InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: FULLER FORD/KIA (Continued)S106064374 TC5146125.2s Page 27 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 134845PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: USEDOILOtherInformation: WASTE 221 WASTE OIL & MIXEDOILName: NotreportedCaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: WASTEGASOLINEOtherInformation: WASTE 214 UNSPEC SOLVENTMIXTUREName: NotreportedCaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: BRAKEWASHEROtherInformation: WASTE 214 UNSPEC SOLVENTMIXTUREName: NotreportedCaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: PARTS CLEANER CLEANINGSOLUTIONOtherInformation: WASTE 133 AQUEOUS SOL’N W/ 10% ORGRESIDName: NotreportedCaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: FIREHazardousCategories1: MaterialMaterialWaste: NotreportedOtherInformation: SOAP-DETAIL CHEMICALS/CASTROLName: MIXTURECaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: PRESSURERELEASEHazardousCategories2: FIREHazardousCategories1: MaterialMaterialWaste: NotreportedOtherInformation: PROPANEName: 68476-85-7CaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: FULLER FORD/KIA (Continued)S106064374 TC5146125.2s Page 28 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 6HV0216ViolationCode: 04/03/2007InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: Did not have adequate employee training program 2732 &/or 25504( c)Violation Citation: EMPLOYEE TRAINING NOTADEQUATEViolation: 6HV1015ViolationCode: 04/03/2007InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: Violations Active Permits: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: CRUSHEDOtherInformation: WASTE 888 USED OILFILTERSName: NotreportedCaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: NotreportedOtherInformation: WASTE 444 USEDBATTERIESName: NotreportedCaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: USED ETHYLENE GLYCOL/COOLANTOtherInformation: WASTE 342 ORGANIC LIQUIDS W/METALSName: NotreportedCaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: OILY RAGS/SATURATEDABSORBENTSOtherInformation: WASTE 223 UNSPEC OIL CONTAININGWASTEName: NotreportedCaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: SLUDGE (OIL&WATER)Other Information: WASTE 222 OIL/WATER SEPARATIONSLUDGEName: NotreportedCaseNumber: 11/02/2012UpdateDate: FULLER FORD/KIA (Continued)S106064374 TC5146125.2s Page 29 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation ACTIVEActivity: 66265.191(a) or 66265.192(a) Failed to obtain a P.E. assessment for hazardous waste tank system.Violation Citation: HAZWASTE TANKS W/O P.E. ASSESSMENTViolation: 6HV1601ViolationCode: 04/03/2007InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: waste is inadequate. CFR 262.34(d)(5)(iii) Employee training program for small quantity generator ofhazardousViolationCitation: EMPLOYEE TRAINING NOTADEQUATEViolation: 6HV0407ViolationCode: 04/03/2007InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: Waste accumulated in a container in poor condition. CFR 265.171ViolationCitation: HW CONTAINER IN POORCONDITIONViolation: 6HV0232ViolationCode: 04/03/2007InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: Failed to keep container closed. CFR 265.173ViolationCitation: CONTAINER NOT KEPTCLOSEDViolation: 6HV0228ViolationCode: 04/03/2007InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: 66262.34(f) Failed to properly label/date hazardous waste container &/or tank.Violation Citation: HAZWASTE TANK/CONTAINER W/O LABEL/DATEViolation: 6HV0227ViolationCode: 04/03/2007InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: from a container. 66261.7 (b), (d) &/or ( r) Failed to properly manage non-empty container or inner linerremovedViolationCitation: MISMANAGED NON-EMPTY CONTAINER/LINERViolation: 6HV0223ViolationCode: 04/03/2007InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: are now declared hazardous waste. HSC 25124(b)(3)(A) & 66262.34(f) Hazardous materials have not been adequately labeled within 10 days &Violation Citation: HAZMATS WITHOUT PROPERLABELSViolation: FULLER FORD/KIA (Continued)S106064374 TC5146125.2s Page 30 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 134845PermitNumber: ACTIVEActivity: 66265.191(a) or 66265.192(a) Failed to obtain a P.E. assessment for hazardous waste tank system.Violation Citation: HAZWASTE TANKS W/O P.E. ASSESSMENTViolation: 6HV1601ViolationCode: 01/12/2004InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: 66265.16(d)&(e) with requirements for current and former employees. CCR Personnel training records are not maintained to documentcomplianceViolationCitation: TRAINING RECORDSUNAVAILABLEViolation: 6HV0401ViolationCode: 01/12/2004InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: explosion or release. CCR 66265.31 Facility not maintained &/operated to minimize possibility of fire,Violation Citation: FIRE/EXPLOSION/RELEASE NOTMINIMIZEDViolation: 6HV0207ViolationCode: 01/12/2004InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: 66262.34(a)(3) & 66262.34(f) date and/or are improperly labeled. CCR 66262.34(a)(2); Hazardous waste containers &/or tanks are missing labels, accumulationViolationCitation: WASTE CONTAINER W/OLABELSViolation: 6HV0202ViolationCode: 01/12/2004InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: 66265.173(a) Hazardous waste containers are not kept closed while in storage. CCRViolationCitation: WASTE CONTAINER NOTCLOSEDViolation: 6HV0201ViolationCode: 01/12/2004InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: 66265.195 ( c) Failed to inspect and/or document daily HW tank system inspections. Violation Citation: NO DAILY TANK INSPECTION/LOGViolation: 6HV1605ViolationCode: 04/03/2007InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: FULLER FORD/KIA (Continued)S106064374 TC5146125.2s Page 31 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedTreatHazWaste: YGenerateHazWaste: NotreportedSubjectToAPSA: NotreportedOwnOrOperateUST: YHandleRegulatedHazmat: NotreportedUSTOwner: 91911FacilityMailingZip: CAFacilityMailingState: CHULAVISTAFacilityMailingCity: 560 AUTO PARKDRFacilityMailingAddress: DOUGLASFULLERFacilityOwner: 11/02/2012DateLastUpdated: 06/30/2013PermitExpiration: OPENPermitStatus: 619-656-2500FacilityTelephone: 07/13/2010LastHMMDInspection: 644-042-04-00APN: CAR000003897EPAIdNumber: 6HK31BusinessType: 134845PermitNumber: ACTIVEActivity: 66265.195 ( c) Failed to inspect and/or document daily HW tank system inspections. Violation Citation: NO DAILY TANK INSPECTION/LOGViolation: 6HV1605ViolationCode: 09/08/2005InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: 66265.191(a) or 66265.192(a) Failed to obtain a P.E. assessment for hazardous waste tank system.Violation Citation: HAZWASTE TANKS W/O P.E. ASSESSMENTViolation: 6HV1601ViolationCode: 09/08/2005InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: waste regulations. CCR 66265.16(a)&(b) Personnel training is not adequate to ensure compliance withhazardousViolationCitation: TRAINING PROGRAM NOTADEQUATEViolation: 6HV0402ViolationCode: 09/08/2005InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: 66262.34(a)&( c) without a State permit or written variance. CCR 25201(a) & Hazardous waste is stored in excess of allowable time period (90 days)Violation Citation: WASTE ONSITE >90/180/270DAYSViolation: 6HV0209ViolationCode: 09/08/2005InspectionDate: 11/02/2012UpdateDate: FULLER FORD/KIA (Continued)S106064374 TC5146125.2s Page 32 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 134845PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: PARTS CLEANER CLEANINGSOLUTIONOtherInformation: WASTE 133 AQUEOUS SOL’N W/ 10% ORGRESIDName: NotreportedCaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: FIREHazardousCategories1: MaterialMaterialWaste: NotreportedOtherInformation: SOAP-DETAIL CHEMICALS/CASTROLName: MIXTURECaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: PRESSURERELEASEHazardousCategories2: FIREHazardousCategories1: MaterialMaterialWaste: NotreportedOtherInformation: PROPANEName: 68476-85-7CaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: FIREHazardousCategories1: MaterialMaterialWaste: NotreportedOtherInformation: LUBRICATING FLUID (BASE LUBRICATING OIL)Name: 647426-65-0CaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: ACUTEHazardousCategories1: MaterialMaterialWaste: NotreportedOtherInformation: LIQUID CAR WASH CONCENTRATE P-181FName: MIXTURECaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: ACUTEHazardousCategories2: PRESSURERELEASEHazardousCategories1: MaterialMaterialWaste: NotreportedOtherInformation: HELIUMName: 7740-59-7CaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: Inventory Active Permits (not SQG Medical): NotreportedGenerateMedicalWaste: FULLER FORD/KIA (Continued)S106064374 TC5146125.2s Page 33 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation WASTE 444 USEDBATTERIESName: NotreportedCaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: USED ETHYLENE GLYCOL/COOLANTOtherInformation: WASTE 342 ORGANIC LIQUIDS W/METALSName: NotreportedCaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: OILY RAGS/SATURATEDABSORBENTSOtherInformation: WASTE 223 UNSPEC OIL CONTAININGWASTEName: NotreportedCaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: SLUDGE (OIL&WATER)Other Information: WASTE 222 OIL/WATER SEPARATIONSLUDGEName: NotreportedCaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: USEDOILOtherInformation: WASTE 221 WASTE OIL & MIXEDOILName: NotreportedCaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: WASTEGASOLINEOtherInformation: WASTE 214 UNSPEC SOLVENTMIXTUREName: NotreportedCaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: BRAKEWASHEROtherInformation: WASTE 214 UNSPEC SOLVENTMIXTUREName: NotreportedCaseNumber: 11/02/2012UpdateDate: FULLER FORD/KIA (Continued)S106064374 TC5146125.2s Page 34 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation ACTIVEActivity: Failed to keep container closed. CFR 265.173ViolationCitation: CONTAINER NOT KEPTCLOSEDViolation: 6HV0228ViolationCode: 04/03/2007InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: 66262.34(f) Failed to properly label/date hazardous waste container &/or tank.Violation Citation: HAZWASTE TANK/CONTAINER W/O LABEL/DATEViolation: 6HV0227ViolationCode: 04/03/2007InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: from a container. 66261.7 (b), (d) &/or ( r) Failed to properly manage non-empty container or inner linerremovedViolationCitation: MISMANAGED NON-EMPTY CONTAINER/LINERViolation: 6HV0223ViolationCode: 04/03/2007InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: are now declared hazardous waste. HSC 25124(b)(3)(A) & 66262.34(f) Hazardous materials have not been adequately labeled within 10 days &Violation Citation: HAZMATS WITHOUT PROPERLABELSViolation: 6HV0216ViolationCode: 04/03/2007InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: Did not have adequate employee training program 2732 &/or 25504( c)Violation Citation: EMPLOYEE TRAINING NOTADEQUATEViolation: 6HV1015ViolationCode: 04/03/2007InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: Violations Active Permits: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: CRUSHEDOtherInformation: WASTE 888 USED OILFILTERSName: NotreportedCaseNumber: 11/02/2012UpdateDate: 134845PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: NotreportedOtherInformation: FULLER FORD/KIA (Continued)S106064374 TC5146125.2s Page 35 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 01/12/2004InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: 66262.34(a)(3) & 66262.34(f) date and/or are improperly labeled. CCR 66262.34(a)(2); Hazardous waste containers &/or tanks are missing labels, accumulationViolationCitation: WASTE CONTAINER W/OLABELSViolation: 6HV0202ViolationCode: 01/12/2004InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: 66265.173(a) Hazardous waste containers are not kept closed while in storage. CCRViolationCitation: WASTE CONTAINER NOTCLOSEDViolation: 6HV0201ViolationCode: 01/12/2004InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: 66265.195 ( c) Failed to inspect and/or document daily HW tank system inspections. Violation Citation: NO DAILY TANK INSPECTION/LOGViolation: 6HV1605ViolationCode: 04/03/2007InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: 66265.191(a) or 66265.192(a) Failed to obtain a P.E. assessment for hazardous waste tank system.Violation Citation: HAZWASTE TANKS W/O P.E. ASSESSMENTViolation: 6HV1601ViolationCode: 04/03/2007InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: waste is inadequate. CFR 262.34(d)(5)(iii) Employee training program for small quantity generator ofhazardousViolationCitation: EMPLOYEE TRAINING NOTADEQUATEViolation: 6HV0407ViolationCode: 04/03/2007InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: Waste accumulated in a container in poor condition. CFR 265.171ViolationCitation: HW CONTAINER IN POORCONDITIONViolation: 6HV0232ViolationCode: 04/03/2007InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: FULLER FORD/KIA (Continued)S106064374 TC5146125.2s Page 36 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 6HV1605ViolationCode: 09/08/2005InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: 66265.191(a) or 66265.192(a) Failed to obtain a P.E. assessment for hazardous waste tank system.Violation Citation: HAZWASTE TANKS W/O P.E. ASSESSMENTViolation: 6HV1601ViolationCode: 09/08/2005InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: waste regulations. CCR 66265.16(a)&(b) Personnel training is not adequate to ensure compliance withhazardousViolationCitation: TRAINING PROGRAM NOTADEQUATEViolation: 6HV0402ViolationCode: 09/08/2005InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: 66262.34(a)&( c) without a State permit or written variance. CCR 25201(a) & Hazardous waste is stored in excess of allowable time period (90 days)Violation Citation: WASTE ONSITE >90/180/270DAYSViolation: 6HV0209ViolationCode: 09/08/2005InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: 66265.191(a) or 66265.192(a) Failed to obtain a P.E. assessment for hazardous waste tank system.Violation Citation: HAZWASTE TANKS W/O P.E. ASSESSMENTViolation: 6HV1601ViolationCode: 01/12/2004InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: 66265.16(d)&(e) with requirements for current and former employees. CCR Personnel training records are not maintained to documentcomplianceViolationCitation: TRAINING RECORDSUNAVAILABLEViolation: 6HV0401ViolationCode: 01/12/2004InspectionDate: 11/02/2012UpdateDate: 134845PermitNumber: ACTIVEActivity: explosion or release. CCR 66265.31 Facility not maintained &/operated to minimize possibility of fire,Violation Citation: FIRE/EXPLOSION/RELEASE NOTMINIMIZEDViolation: 6HV0207ViolationCode: FULLER FORD/KIA (Continued)S106064374 TC5146125.2s Page 37 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation ACTIVEActivity: 66265.195 ( c) Failed to inspect and/or document daily HW tank system inspections. Violation Citation: NO DAILY TANK INSPECTION/LOGViolation: FULLER FORD/KIA (Continued)S106064374 NoOn-site burner exemption: NoUndergroundinjectionactivity: NoTreater, storer or disposer of HW: NoTransporterofhazardouswaste: NoRecyclerofhazardouswaste: NoMixedwaste (haz. and radioactive): NoU.S. importer of hazardous waste: Handler Activities Summary: NotreportedOwner/Op end date: NotreportedOwner/Op start date: OwnerOwner/Operator Type: PrivateLegalstatus: NotreportedOwner/operator extension: NotreportedOwner/operator fax: NotreportedOwner/operator email: 619-656-2500Owner/operator telephone: NotreportedOwner/operator country: CHULA VISTA, CA 91911 540 AUTO PARKDROwner/operator address: DOUGLASFULLEROwner/operator name: Owner/Operator Summary: hazardous waste at any time waste during any calendar month, and accumulates more than 1000 kg of hazardous waste at any time; or generates 100 kg or less of hazardous waste during any calendar month and accumulates less than 6000 kg of Handler: generates more than 100 and less than 1000 kg ofhazardousDescription: Small Small QuantityGeneratorClassification: PrivateLandtype: 09EPARegion: NotreportedContactemail: 619-656-2500Contacttelephone: USContactcountry: CHULA VISTA, CA 91911 540 AUTO PARKDRContactaddress: ANDYPAREDESContact: CHULA VISTA, CA 91911 AUTO PARKDRMailingaddress: CAR000003897EPAID: CHULA VISTA, CA 91911 560 AUTO PARKDRFacilityaddress: FULLER FORDHONDAFacilityname: 06/27/1995Dateformreceivedbyagency: RCRA-SQG: 736 ft.CAHAZNETSite3of3inclusterD 0.139 mi.CA EMI Relative: Lower Actual: 130 ft. 1/8-1/4 ECHOCHULAVISTA, CA 91911 SSE FINDS560AUTOPARKDR CAR000003897 D11 RCRA-SQGFULLERFORDHONDA 1001023038 TC5146125.2s Page 38 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation California Hazardous Waste Tracking System - Datamart (HWTS-DATAMART) Environmental Interest/Information System 110002906785RegistryID: FINDS: State Contractor/GranteeEvaluationleadagency: 01/12/2004Dateachievedcompliance: Generators - GeneralAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 01/12/2004Evaluationdate: State Contractor/GranteeEvaluationleadagency: 01/22/2004Dateachievedcompliance: Generators - GeneralAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 01/12/2004Evaluationdate: Evaluation Action Summary: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: Not reportedEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: Not reportedEnforcementactiondate: Not reportedEnforcementaction: StateViolationleadagency: 01/22/2004Dateachievedcompliance: 01/12/2004Dateviolationdetermined: Generators - GeneralAreaofviolation: NotreportedRegulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: Not reportedEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: Not reportedEnforcementactiondate: Not reportedEnforcementaction: StateViolationleadagency: 01/12/2004Dateachievedcompliance: 01/12/2004Dateviolationdetermined: Generators - GeneralAreaofviolation: NotreportedRegulationviolated: Facility Has Received Notices of Violations: NoUsedoiltransporter: NoUsedoiltransferfacility: NoUsedoilSpecificationmarketer: NoUsedoilfuelmarketertoburner: NoUseroilrefiner: NoUsedoilprocessor: NoUsedoilfuelburner: NoFurnaceexemption: FULLER FORD HONDA (Continued)1001023038 TC5146125.2s Page 39 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 0Part. Matter 10 Micrometers and Smllr Tons/Yr: 0ParticulateMatterTons/Yr: 0SOX - Oxides of Sulphur Tons/Yr: 0NOX - Oxides of Nitrogen Tons/Yr: 0CarbonMonoxideEmissionsTons/Yr: 1ReactiveOrganicGasesTons/Yr: 1TotalOrganicHydrocarbonGasesTons/Yr: NotreportedConsolidatedEmissionReportingRule: NotreportedCommunityHealthAirPollutionInfoSystem: SAN DIEGO COUNTYAPCDAirDistrictName: 7532SICCode: SDAirDistrictName: 94014FacilityID: SDAirBasin: 37CountyCode: 2000Year: 0Part. Matter 10 Micrometers and Smllr Tons/Yr: 0ParticulateMatterTons/Yr: 0SOX - Oxides of Sulphur Tons/Yr: 0NOX - Oxides of Nitrogen Tons/Yr: 0CarbonMonoxideEmissionsTons/Yr: 1ReactiveOrganicGasesTons/Yr: 1TotalOrganicHydrocarbonGasesTons/Yr: NotreportedConsolidatedEmissionReportingRule: NotreportedCommunityHealthAirPollutionInfoSystem: SAN DIEGO COUNTYAPCDAirDistrictName: 7532SICCode: SDAirDistrictName: 94014FacilityID: SDAirBasin: 37CountyCode: 1999Year: EMI: http://echo.epa.gov/detailed-facility-report?fid=110002906785DFRURL: 110002906785RegistryID: 1001023038Envid: ECHO: additional FINDS: detail in the EDR Site Report. Click this hyperlink while viewing on your computer to access HAZARDOUS AIR POLLUTANT MAJOR corrective action activities required under RCRA. program staff to track the notification, permit, compliance, and and treat, store, or dispose of hazardous waste. RCRAInfo allows RCRA events and activities related to facilities that generate, transport, Conservation and Recovery Act (RCRA) program through the tracking of RCRAInfo is a national information system that supports the Resource facilities. generators, transporters, and treatment, storage, and disposal provides California with information on hazardous waste shipments for FULLER FORD HONDA (Continued)1001023038 TC5146125.2s Page 40 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 7532SICCode: SDAirDistrictName: 94014FacilityID: SDAirBasin: 37CountyCode: 2004Year: 0Part. Matter 10 Micrometers and Smllr Tons/Yr: 0ParticulateMatterTons/Yr: 0SOX - Oxides of Sulphur Tons/Yr: 0NOX - Oxides of Nitrogen Tons/Yr: 0CarbonMonoxideEmissionsTons/Yr: 1ReactiveOrganicGasesTons/Yr: 1TotalOrganicHydrocarbonGasesTons/Yr: NotreportedConsolidatedEmissionReportingRule: NotreportedCommunityHealthAirPollutionInfoSystem: SAN DIEGO COUNTYAPCDAirDistrictName: 7532SICCode: SDAirDistrictName: 94014FacilityID: SDAirBasin: 37CountyCode: 2003Year: 0Part. Matter 10 Micrometers and Smllr Tons/Yr: 0ParticulateMatterTons/Yr: 0SOX - Oxides of Sulphur Tons/Yr: 0NOX - Oxides of Nitrogen Tons/Yr: 0CarbonMonoxideEmissionsTons/Yr: 1ReactiveOrganicGasesTons/Yr: 1TotalOrganicHydrocarbonGasesTons/Yr: NotreportedConsolidatedEmissionReportingRule: NotreportedCommunityHealthAirPollutionInfoSystem: SAN DIEGO COUNTYAPCDAirDistrictName: 7532SICCode: SDAirDistrictName: 94014FacilityID: SDAirBasin: 37CountyCode: 2002Year: 0Part. Matter 10 Micrometers and Smllr Tons/Yr: 0ParticulateMatterTons/Yr: 0SOX - Oxides of Sulphur Tons/Yr: 0NOX - Oxides of Nitrogen Tons/Yr: 0CarbonMonoxideEmissionsTons/Yr: 1ReactiveOrganicGasesTons/Yr: 1TotalOrganicHydrocarbonGasesTons/Yr: NotreportedConsolidatedEmissionReportingRule: NotreportedCommunityHealthAirPollutionInfoSystem: SAN DIEGO COUNTYAPCDAirDistrictName: 7532SICCode: SDAirDistrictName: 94014FacilityID: SDAirBasin: 37CountyCode: 2001Year: FULLER FORD HONDA (Continued)1001023038 TC5146125.2s Page 41 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 0CarbonMonoxideEmissionsTons/Yr: 66ReactiveOrganicGasesTons/Yr: 69TotalOrganicHydrocarbonGasesTons/Yr: NotreportedConsolidatedEmissionReportingRule: NotreportedCommunityHealthAirPollutionInfoSystem: SAN DIEGO COUNTYAPCDAirDistrictName: 7532SICCode: SDAirDistrictName: 94014FacilityID: SDAirBasin: 37CountyCode: 2007Year: 0Part. Matter 10 Micrometers and Smllr Tons/Yr: 0ParticulateMatterTons/Yr: 0SOX - Oxides of Sulphur Tons/Yr: 0NOX - Oxides of Nitrogen Tons/Yr: 0CarbonMonoxideEmissionsTons/Yr: 66ReactiveOrganicGasesTons/Yr: 69TotalOrganicHydrocarbonGasesTons/Yr: NotreportedConsolidatedEmissionReportingRule: NotreportedCommunityHealthAirPollutionInfoSystem: SAN DIEGO COUNTYAPCDAirDistrictName: 7532SICCode: SDAirDistrictName: 94014FacilityID: SDAirBasin: 37CountyCode: 2006Year: 0Part. Matter 10 Micrometers and Smllr Tons/Yr: 0ParticulateMatterTons/Yr: 0SOX - Oxides of Sulphur Tons/Yr: 0NOX - Oxides of Nitrogen Tons/Yr: 0CarbonMonoxideEmissionsTons/Yr: 9718977ReactiveOrganicGasesTons/Yr: 1.05376546TotalOrganicHydrocarbonGasesTons/Yr: NotreportedConsolidatedEmissionReportingRule: NotreportedCommunityHealthAirPollutionInfoSystem: SAN DIEGO COUNTYAPCDAirDistrictName: 7532SICCode: SDAirDistrictName: 94014FacilityID: SDAirBasin: 37CountyCode: 2005Year: 0Part. Matter 10 Micrometers and Smllr Tons/Yr: 0ParticulateMatterTons/Yr: 0SOX - Oxides of Sulphur Tons/Yr: 0NOX - Oxides of Nitrogen Tons/Yr: 0CarbonMonoxideEmissionsTons/Yr: 0.9718977ReactiveOrganicGasesTons/Yr: 1.05376546TotalOrganicHydrocarbonGasesTons/Yr: NotreportedConsolidatedEmissionReportingRule: NotreportedCommunityHealthAirPollutionInfoSystem: SAN DIEGO COUNTYAPCDAirDistrictName: FULLER FORD HONDA (Continued)1001023038 TC5146125.2s Page 42 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 0Part. Matter 10 Micrometers and Smllr Tons/Yr: 0ParticulateMatterTons/Yr: 0SOX - Oxides of Sulphur Tons/Yr: 0NOX - Oxides of Nitrogen Tons/Yr: 0CarbonMonoxideEmissionsTons/Yr: 0.66000000000000003ReactiveOrganicGasesTons/Yr: 0.68999999999999995TotalOrganicHydrocarbonGasesTons/Yr: NotreportedConsolidatedEmissionReportingRule: NotreportedCommunityHealthAirPollutionInfoSystem: SAN DIEGO COUNTYAPCDAirDistrictName: 7532SICCode: SDAirDistrictName: 94014FacilityID: SDAirBasin: 37CountyCode: 2010Year: 0Part. Matter 10 Micrometers and Smllr Tons/Yr: 0ParticulateMatterTons/Yr: 0SOX - Oxides of Sulphur Tons/Yr: 0NOX - Oxides of Nitrogen Tons/Yr: 0CarbonMonoxideEmissionsTons/Yr: 0.66000000000000003ReactiveOrganicGasesTons/Yr: 0.68999999999999995TotalOrganicHydrocarbonGasesTons/Yr: NotreportedConsolidatedEmissionReportingRule: NotreportedCommunityHealthAirPollutionInfoSystem: SAN DIEGO COUNTYAPCDAirDistrictName: 7532SICCode: SDAirDistrictName: 94014FacilityID: SDAirBasin: 37CountyCode: 2009Year: 0Part. Matter 10 Micrometers and Smllr Tons/Yr: 0ParticulateMatterTons/Yr: 0SOX - Oxides of Sulphur Tons/Yr: 0NOX - Oxides of Nitrogen Tons/Yr: 0CarbonMonoxideEmissionsTons/Yr: 66ReactiveOrganicGasesTons/Yr: 69TotalOrganicHydrocarbonGasesTons/Yr: NotreportedConsolidatedEmissionReportingRule: NotreportedCommunityHealthAirPollutionInfoSystem: SAN DIEGO COUNTYAPCDAirDistrictName: 7532SICCode: SDAirDistrictName: 94014FacilityID: SDAirBasin: 37CountyCode: 2008Year: 0Part. Matter 10 Micrometers and Smllr Tons/Yr: 0ParticulateMatterTons/Yr: 0SOX - Oxides of Sulphur Tons/Yr: 0NOX - Oxides of Nitrogen Tons/Yr: FULLER FORD HONDA (Continued)1001023038 TC5146125.2s Page 43 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation Unspecified organic liquidmixtureCatDecode: 0.374Tons: Organics Recovery Ect Other Recovery Of Reclamation For Reuse Including Acid Regeneration,Disposal Method: Unspecified organic liquidmixtureWasteCategory: LosAngelesTSDCounty: CAT080013352TSDEPAID: SanDiegoGenCounty: CHULA VISTA, CA919116026MailingCity,St,Zip: 560 AUTO PARKDRMailingAddress: NotreportedMailingName: 6196563317Telephone: DAVIDWARDContact: CAR000003897GEPAID: 2016Year: 1001023038envid: SanDiegoFacilityCounty: H010-H129) Or (H131-H135) Storage, Bulking, And/Or Transfer Off Site--No Treatment/ReoveryMethodDecode: Other organicsolidsCatDecode: 0.075Tons: H010-H129) Or (H131-H135) Storage, Bulking, And/Or Transfer Off Site--No Treatment/ReoveryDisposalMethod: Other organicsolidsWasteCategory: 99TSDCounty: AZR000515924TSDEPAID: SanDiegoGenCounty: CHULA VISTA, CA919116026MailingCity,St,Zip: 560 AUTO PARKDRMailingAddress: NotreportedMailingName: 6196563317Telephone: DAVIDWARDContact: CAR000003897GEPAID: 2016Year: 1001023038envid: SanDiegoFacilityCounty: H010-H129) Or (H131-H135) Storage, Bulking, And/Or Transfer Off Site--No Treatment/ReoveryMethodDecode: Oxygenated solvents (acetone, butanol, ethyl acetate, etc.)Cat Decode: 0.0415Tons: H010-H129) Or (H131-H135) Storage, Bulking, And/Or Transfer Off Site--No Treatment/ReoveryDisposalMethod: Oxygenated solvents (acetone, butanol, ethyl acetate, etc.)Waste Category: LosAngelesTSDCounty: CAD044429835TSDEPAID: SanDiegoGenCounty: CHULA VISTA, CA919116026MailingCity,St,Zip: 560 AUTO PARKDRMailingAddress: NotreportedMailingName: 6196563317Telephone: DAVIDWARDContact: CAR000003897GEPAID: 2016Year: 1001023038envid: HAZNET: FULLER FORD HONDA (Continued)1001023038 TC5146125.2s Page 44 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 236 additional CA_HAZNET: record(s) in the EDR Site Report. Click this hyperlink while viewing on your computer to access SanDiegoFacilityCounty: NotreportedMethodDecode: NotreportedCatDecode: 0.1251Tons: Organics Recovery Ect Other Recovery Of Reclamation For Reuse Including Acid Regeneration,Disposal Method: Unspecified oil-containingwasteWasteCategory: LosAngelesTSDCounty: CAT080013352TSDEPAID: SanDiegoGenCounty: CHULA VISTA, CA919116026MailingCity,St,Zip: 560 AUTO PARKDRMailingAddress: NotreportedMailingName: 6196563317Telephone: DAVIDWARDContact: CAR000003897GEPAID: 2015Year: 1001023038envid: SanDiegoFacilityCounty: H010-H129) Or (H131-H135) Storage, Bulking, And/Or Transfer Off Site--No Treatment/ReoveryMethodDecode: Aqueous solution with total organic residues less than 10percentCatDecode: 0.6636Tons: H010-H129) Or (H131-H135) Storage, Bulking, And/Or Transfer Off Site--No Treatment/ReoveryDisposalMethod: Aqueous solution with total organic residues less than 10percentWasteCategory: OrangeTSDCounty: CAT000613976TSDEPAID: SanDiegoGenCounty: CHULA VISTA, CA919116026MailingCity,St,Zip: 560 AUTO PARKDRMailingAddress: NotreportedMailingName: 6196563317Telephone: DAVIDWARDContact: CAR000003897GEPAID: 2016Year: 1001023038envid: SanDiegoFacilityCounty: Organics Recovery Ect Other Recovery Of Reclamation For Reuse Including Acid Regeneration,Method Decode: FULLER FORD HONDA (Continued)1001023038 CAD983652314EPAID: CHULA VISTA, CA 91911 1669 BRANDYWINE AVE STEAFacilityaddress: RAYCHEMCORPFacilityname: 06/28/2001Dateformreceivedbyagency: RCRA NonGen / NLR: 751 ft. 0.142 mi.CA HAZNET Relative: Higher Actual: 208 ft. 1/8-1/4 ECHOCHULAVISTA, CA 91911 East FINDS1669BRANDYWINEAVESTEA CAD983652314 12 RCRA NonGen / NLRRAYCHEMCORP 1000819257 TC5146125.2s Page 45 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation corrective action activities required under RCRA. program staff to track the notification, permit, compliance, and and treat, store, or dispose of hazardous waste. RCRAInfo allows RCRA events and activities related to facilities that generate, transport, Conservation and Recovery Act (RCRA) program through the tracking of RCRAInfo is a national information system that supports the Resource Environmental Interest/Information System 110002887298RegistryID: FINDS: No violationsfoundViolationStatus: NoUsedoiltransporter: NoUsedoiltransferfacility: NoUsedoilSpecificationmarketer: NoUsedoilfuelmarketertoburner: NoUseroilrefiner: NoUsedoilprocessor: NoUsedoilfuelburner: NoFurnaceexemption: NoOn-site burner exemption: NoUndergroundinjectionactivity: NoTreater, storer or disposer of HW: NoTransporterofhazardouswaste: NoRecyclerofhazardouswaste: NoMixedwaste (haz. and radioactive): NoU.S. importer of hazardous waste: Handler Activities Summary: NotreportedOwner/Op end date: NotreportedOwner/Op start date: OwnerOwner/Operator Type: PrivateLegalstatus: NotreportedOwner/operator extension: NotreportedOwner/operator fax: NotreportedOwner/operator email: 619-546-5151Owner/operator telephone: NotreportedOwner/operator country: SAN DIEGO, CA 92122 4350 LA JOLLA VILLAGE DR210Owner/operator address: SUDBERRYPROPERTIESOwner/operator name: Owner/Operator Summary: Handler: Non-Generators do not presently generate hazardouswasteDescription: Non-GeneratorClassification: 09EPARegion: NotreportedContactemail: 619-424-4237Contacttelephone: USContactcountry: CHULA VISTA, CA 91911 1675 BRANDYWINE AVE STECContactaddress: MARTINORIGUELContact: RAYCHEM CORP (Continued)1000819257 TC5146125.2s Page 46 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation CAT080014079TSDEPAID: NotreportedGenCounty: MENLO PARK, CA940251140MailingCity,St,Zip: 300 CONSTITUTION DRIVE MS 106/2BMailingAddress: NotreportedMailingName: 6503613333Telephone: RAYCHEMCORPContact: CAD983652314GEPAID: 1998Year: 1000819257envid: SanDiegoFacilityCounty: NotreportedMethodDecode: NotreportedCatDecode: 1.2500Tons: TransferStationDisposalMethod: Off-specification, aged or surplusorganicsWasteCategory: NotreportedTSDCounty: CAT080014079TSDEPAID: NotreportedGenCounty: MENLO PARK, CA940251140MailingCity,St,Zip: 300 CONSTITUTION DRIVE MS 106/2BMailingAddress: NotreportedMailingName: 6503613333Telephone: RAYCHEMCORPContact: CAD983652314GEPAID: 1998Year: 1000819257envid: SanDiegoFacilityCounty: NotreportedMethodDecode: NotreportedCatDecode: 3753Tons: Disposal, OtherDisposalMethod: Off-specification, aged or surplusorganicsWasteCategory: NotreportedTSDCounty: CAD044429835TSDEPAID: NotreportedGenCounty: MENLO PARK, CA940251140MailingCity,St,Zip: 300 CONSTITUTION DRIVE MS 106/2BMailingAddress: NotreportedMailingName: 6503613333Telephone: RAYCHEMCORPContact: CAD983652314GEPAID: 1999Year: 1000819257envid: HAZNET: http://echo.epa.gov/detailed-facility-report?fid=110002887298DFRURL: 110002887298RegistryID: 1000819257Envid: ECHO: additional FINDS: detail in the EDR Site Report. Click this hyperlink while viewing on your computer to access RAYCHEM CORP (Continued)1000819257 TC5146125.2s Page 47 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 12 additional CA_HAZNET: record(s) in the EDR Site Report. Click this hyperlink while viewing on your computer to access SanDiegoFacilityCounty: NotreportedMethodDecode: NotreportedCatDecode: 2000Tons: TransferStationDisposalMethod: Other empty containers 30 gallons ormoreWasteCategory: NotreportedTSDCounty: CAD050806850TSDEPAID: NotreportedGenCounty: MENLO PARK, CA940251140MailingCity,St,Zip: 300 CONSTITUTION DRIVE MS 106/2BMailingAddress: NotreportedMailingName: 6503613333Telephone: RAYCHEMCORPContact: CAD983652314GEPAID: 1997Year: 1000819257envid: SanDiegoFacilityCounty: NotreportedMethodDecode: NotreportedCatDecode: 4000Tons: RecyclerDisposalMethod: Off-specification, aged or surplusorganicsWasteCategory: NotreportedTSDCounty: CAD008302903TSDEPAID: NotreportedGenCounty: MENLO PARK, CA940251140MailingCity,St,Zip: 300 CONSTITUTION DRIVE MS 106/2BMailingAddress: NotreportedMailingName: 6503613333Telephone: RAYCHEMCORPContact: CAD983652314GEPAID: 1998Year: 1000819257envid: SanDiegoFacilityCounty: NotreportedMethodDecode: NotreportedCatDecode: 2000Tons: TransferStationDisposalMethod: Other inorganic solidwasteWasteCategory: NotreportedTSDCounty: RAYCHEM CORP (Continued)1000819257 T0607300404GlobalId: http://geotracker.waterboards.ca.gov/profile_report.asp?global_id=T0607300404GeoTrack: LUST CleanupSiteCaseType: SAN DIEGO COUNTYLOPLeadAgency: LUST: 763 ft. Site 1 of 3 in cluster E 0.145 mi.CA HIST CORTESE Relative: Lower Actual: 137 ft. 1/8-1/4 CA SWEEPSUSTCHULAVISTA, CA 91911 SW CA SAN DIEGO CO. SAM490OTAYVALLEYRD N/A E13 CALUSTPACIFICBELL 1000250089 TC5146125.2s Page 48 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation UnknownCause: TankSource: CloseTankHowStopped: TankClosureHowFound: SanDiegoLocalAgency: No Action Required - incident is minor, requiring no remedialactionAbateMethod: NotreportedQtyLeaked: WasteOilSubstance: H14060-001LocalCase: 9UT1584CaseNumber: CaseClosedStatus: 9Region: LUST REG 9: 11/08/1989StatusDate: Open - Case BeginDateStatus: T0607300404GlobalId: 02/22/1991StatusDate: Completed - CaseClosedStatus: T0607300404GlobalId: LUST: LeakDiscoveryAction: 11/08/1989Date: OtherActionType: T0607300404GlobalId: LeakBeganAction: 11/08/1989Date: OtherActionType: T0607300404GlobalId: LeakStoppedAction: 11/08/1989Date: OtherActionType: T0607300404GlobalId: LeakReportedAction: 11/08/1989Date: OtherActionType: T0607300404GlobalId: LUST: NotreportedSiteHistory: Waste Oil / Motor / Hydraulic / LubricatingPotentialContaminantsofConcern: SoilPotentialMediaAffect: H14060-001LocalCaseNumber: LocalAgencyFileLocation: NotreportedLocalAgency: 9UT1584RBCaseNumber: NotreportedCaseWorker: 02/22/1991StatusDate: Completed - CaseClosedStatus: 117.000166717794Longitude: 32.5793785288964Latitude: PACIFIC BELL (Continued)1000250089 TC5146125.2s Page 49 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 9Number: 14060CompNumber: ActiveStatus: 1NumberOfTanks: NotreportedContent: WASTESTG: PETROLEUMTankUse: NotreportedActiveDate: 500Capacity: NotreportedTankStatus: 37-000-014060-000001SWRCBTankId: NotreportedOwnerTankId: NotreportedCreatedDate: NotreportedActionDate: NotreportedReferralDate: 44-001027BoardOfEqualization: NotreportedNumber: 14060CompNumber: NotreportedStatus: SWEEPS UST: 11/8/1989DateBegan: 2/22/1991Date: ClosedCaseFacilityStatus: SoilsOnlyFacilityType: LOP - StateFundFunding: DEH Site Assessment & MitigationAgency: H14060-001CaseNumber: SAN DIEGO CO. SAM: NotreportedWasteDischargeRequirementNumber: NotreportedCleanupandAbatementorderNumber: YesInterimRemedialActions: File discarded, caseclosedFileDispn: Low priority. Priority ranking can change over time.Priority: NotreportedNPDESNumber: NotreportedBeneficialUse: NotreportedGWDepth: 910.20BasinNumber: LOPPilotProgram: NotreportedEnforceType: 2/14/91ClosedDate: NotreportedEnforceDate: 11/21/1989ReleaseDate: NotreportedBeganMonitor: NotreportedRemedAction: Remed Plan: NotreportedDescPollution: Prelim Assess: NotreportedSubmitWorkplan: 11/28/1989ConfirmDate: 11/08/1989DateStopped: 11/28/1989DateFound: SoilonlyCaseType: LocalAgencyLeadAgency: PACIFIC BELL (Continued)1000250089 TC5146125.2s Page 50 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 9UT1584RegId: LTNKARegBy: 37FacilityCountyCode: CORTESERegion: HIST CORTESE: NotreportedNumberOfTanks: NotreportedContent: NotreportedSTG: NotreportedTankUse: NotreportedActiveDate: NotreportedCapacity: NotreportedTankStatus: NotreportedSWRCBTankId: NotreportedOwnerTankId: 02-29-88CreatedDate: 06-26-92ActionDate: NotreportedReferralDate: 44-001027BoardOfEqualization: PACIFIC BELL (Continued)1000250089 117.0334027Longitude: 32.5957496Latitude: SAN DIEGOCOUNTYPermittingAgency: H02893FacilityID: UST: 936 ft. Site 2 of 3 in cluster E 0.177 mi. Relative: Lower Actual: 140 ft. 1/8-1/4 CHULA VISTA, CA 91911 SW 4555 MAIN ST N/A E14 CAUSTS & L SHELL MART U003941434 4NumberOfTanks: REGUNLEADEDContent: PSTG: M.V. FUELTankUse: NotreportedActiveDate: 10000Capacity: ATankStatus: 37-000-002893-000001SWRCBTankId: NotreportedOwnerTankId: 02-29-88CreatedDate: 06-26-92ActionDate: NotreportedReferralDate: 44-000074BoardOfEqualization: 9Number: 2893CompNumber: ActiveStatus: SWEEPS UST: 965 ft. Site 1 of 3 in cluster F 0.183 mi. Relative: Lower Actual: 139 ft. 1/8-1/4 CHULA VISTA, CA 91911 SW 4555 OTAY VALLEYRD N/A F15 CA SWEEPSUSTSHELLOILINC S106932098 TC5146125.2s Page 51 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedNumberOfTanks: LEADEDContent: PSTG: M.V. FUELTankUse: NotreportedActiveDate: 10000Capacity: ATankStatus: 37-000-002893-000003SWRCBTankId: NotreportedOwnerTankId: 02-29-88CreatedDate: 06-26-92ActionDate: NotreportedReferralDate: 44-000074BoardOfEqualization: 9Number: 2893CompNumber: ActiveStatus: NotreportedNumberOfTanks: LEADEDContent: PSTG: M.V. FUELTankUse: NotreportedActiveDate: 10000Capacity: ATankStatus: 37-000-002893-000002SWRCBTankId: NotreportedOwnerTankId: 02-29-88CreatedDate: 06-26-92ActionDate: NotreportedReferralDate: 44-000074BoardOfEqualization: 9Number: 2893CompNumber: ActiveStatus: SHELL OIL INC (Continued)S106932098 underground storage tanks (USTs), four fuel dispenser islands with The Site is an active service station consisting of threefuelSiteHistory: GasolinePotentialContaminantsofConcern: Aquifer used for drinking watersupplyPotentialMediaAffect: H02893-001LocalCaseNumber: LocalAgencyFileLocation: SAN DIEGO COUNTYLOPLocalAgency: NotreportedRBCaseNumber: JSCaseWorker: 08/30/2012StatusDate: Completed - CaseClosedStatus: 117.034649848938Longitude: 32.5945590185637Latitude: T0607367594GlobalId: http://geotracker.waterboards.ca.gov/profile_report.asp?global_id=T0607367594GeoTrack: LUST CleanupSiteCaseType: SAN DIEGO COUNTYLOPLeadAgency: LUST: 982 ft. Site 3 of 3 in cluster E 0.186 mi. Relative: Lower Actual: 134 ft. 1/8-1/4 CHULA VISTA, CA 91911 SW CA SAN DIEGO CO. SAM4555AUTOPARKDR N/A E16 CALUSTSHELL S106874378 TC5146125.2s Page 52 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation T0607367594GlobalId: Notice ofResponsibilityAction: 03/13/2003Date: ENFORCEMENTActionType: T0607367594GlobalId: LUST: NotreportedPhoneNumber: jon.senaha@sdcounty.ca.govEmail: SanDiegoCity: P.O. Box129261Address: SAN DIEGO COUNTYLOPOrganizationName: JONSENAHAContactName: Local AgencyCaseworkerContactType: T0607367594GlobalId: LUST: conclusion. risk to human health and the environment. DEH concurs with this consultants registered professional, the Site presents no significant 23, 2012. DEH received no comments. According to the environmental for the CAP was completed. The public comment period ended on March action with regulatory case closure. The Public Participation process concludes that the most appropriate remedial option is no further Action Plan (CAP) was submitted on October 21, 2011. The CAP inhalation risk to the occupants of both buildings. A Corrective from soil and groundwater contamination does not pose a vapor adjacent property to the east). Based on the model results, vapor occupants and to the offsite Soup Plantation building workers (on the health risk associated with soil vapor intrusion to Site building DEH vapor risk model was utilized to evaluate the potential human their water quality objectives by 2049 and 2040, respectively. The analysis indicates that MTBE and TBA in groundwater will drop below environmental consultant analyzed the trends for MTBE and TBA. The plume is stable and the overall mass of impacts is decreasing. The centered on well MW-3 and is mostly contained onsite. The dissolved TPHg), MTBE and TBA. The dissolved phase groundwater plume is impacts include dissolved total petroleum hydrocarbons as gasoline dissolved-phase groundwater plume is adequately assessed. Groundwater groundwater since sampling began in December 2003. The January 2012. No liquid-phase hydrocarbons have been present in Site. Groundwater was monitored and sampled between December 2003 and mg/kg. Nine groundwater monitoring wells have been installed at the residual total petroleum hydrocarbon-impacted soil that is above 100 mostly localized around the UST cavity. There is no remaining and tertiary butyl ether (TBA). Distribution of soil contamination is concern in soil at the Site are methyl tertiary butyl ether (MTBE) xylene were detected in soil at the Site. The main constituents of concentrations and low concentrations of toluene, ethylbenzene and of Environmental Health (DEH) in March 2003. No benzene and unauthorized release case H02893-001 was opened by the Department activities. Petroleum hydrocarbon contamination was detected in soil samples from beneath the dispenser islands and USTs during upgrade product piping were removed. Wayne Perry collected fourteen soil 2002, four 10,000-gallon USTs, five dispenser islands, and associated associated product piping, and a station building. On December 12, SHELL (Continued)S106874378 TC5146125.2s Page 53 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 12/12/2002Date: OtherActionType: T0607367594GlobalId: Technical Correspondence / Assistance / OtherAction: 07/18/2012Date: ENFORCEMENTActionType: T0607367594GlobalId: Monitoring Report - Semi-AnnuallyAction: 10/29/2010Date: RESPONSEActionType: T0607367594GlobalId: Site AssessmentReportAction: 09/03/2010Date: RESPONSEActionType: T0607367594GlobalId: Monitoring Report - Semi-AnnuallyAction: 03/27/2012Date: RESPONSEActionType: T0607367594GlobalId: Monitoring Report - QuarterlyAction: 05/26/2009Date: RESPONSEActionType: T0607367594GlobalId: LeakReportedAction: 02/26/2003Date: OtherActionType: T0607367594GlobalId: Technical Correspondence / Assistance / OtherAction: 07/25/2012Date: ENFORCEMENTActionType: T0607367594GlobalId: Technical Correspondence / Assistance / OtherAction: 01/19/2012Date: ENFORCEMENTActionType: T0607367594GlobalId: Technical Correspondence / Assistance / OtherAction: 01/24/2012Date: ENFORCEMENTActionType: T0607367594GlobalId: Monitoring Report - QuarterlyAction: 04/03/2009Date: RESPONSEActionType: T0607367594GlobalId: Notice ofResponsibilityAction: 04/06/2010Date: ENFORCEMENTActionType: SHELL (Continued)S106874378 TC5146125.2s Page 54 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation CAP/RAP - OtherReportAction: 02/15/2012Date: RESPONSEActionType: T0607367594GlobalId: LeakBeganAction: 12/12/2002Date: OtherActionType: T0607367594GlobalId: Monitoring Report - QuarterlyAction: 10/09/2009Date: RESPONSEActionType: T0607367594GlobalId: LeakStoppedAction: 03/04/2003Date: OtherActionType: T0607367594GlobalId: Letter - NoticeAction: 07/14/2009Date: ENFORCEMENTActionType: T0607367594GlobalId: Monitoring Report - Semi-AnnuallyAction: 04/29/2011Date: RESPONSEActionType: T0607367594GlobalId: Monitoring Report - Semi-AnnuallyAction: 09/21/2011Date: RESPONSEActionType: T0607367594GlobalId: Closure/No Further ActionLetterAction: 08/30/2012Date: ENFORCEMENTActionType: T0607367594GlobalId: Notice ofResponsibilityAction: 07/18/2012Date: ENFORCEMENTActionType: T0607367594GlobalId: Technical Correspondence / Assistance / OtherAction: 07/18/2012Date: ENFORCEMENTActionType: T0607367594GlobalId: Monitoring Report - Semi-AnnuallyAction: 04/27/2010Date: RESPONSEActionType: T0607367594GlobalId: LeakDiscoveryAction: SHELL (Continued)S106874378 TC5146125.2s Page 55 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 12/12/2002DateBegan: 9/28/2004Date: RemedialInvestigationFacilityStatus: Drinking Water AquiferImpactedFacilityType: LOP - StateFundFunding: DEH Site Assessment & MitigationAgency: H02893-001CaseNumber: SAN DIEGO CO. SAM: 05/12/2009StatusDate: Open - SiteAssessmentStatus: T0607367594GlobalId: 09/28/2004StatusDate: Open - RemediationStatus: T0607367594GlobalId: 12/12/2002StatusDate: Open - Case BeginDateStatus: T0607367594GlobalId: 08/30/2012StatusDate: Completed - CaseClosedStatus: T0607367594GlobalId: LUST: CAP/RAP - Other Report - RegulatorRespondedAction: 10/21/2011Date: RESPONSEActionType: T0607367594GlobalId: CorrespondenceAction: 03/29/2012Date: RESPONSEActionType: T0607367594GlobalId: SHELL (Continued)S106874378 0003TotalTanks: ANAHEIM, CA92803OwnerCity,St,Zip: P.O. BOX4848OwnerAddress: SHELL OILCOMPANYOwnerName: 6194216953Telephone: SAMEContactName: NotreportedOtherType: GasStationFacilityType: 00000044031FacilityID: STATERegion: http://geotracker.waterboards.ca.gov/ustpdfs/pdf/0002F314.pdfURL: 0002F314FileNumber: HIST UST: 1071 ft. Site 2 of 3 in cluster F 0.203 mi. Relative: Lower Actual: 139 ft. 1/8-1/4 CHULA VISTA, CA 92011 SW 455 OTAY VALLEY RD N/A F17 CA HISTUSTOTAYVALLEYSHELLSVCINC U001571104 TC5146125.2s Page 56 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation Click here for Geo Tracker PDF: Stock Inventor, Groundwater Monitoring Well, 10LeakDetection: 1/4ContainerConstructionThickness: PREMIUMTypeofFuel: PRODUCTTankUsedfor: 00010000TankCapacity: 1978YearInstalled: 3ContainerNum: 003TankNum: Stock Inventor, Groundwater Monitoring Well, 10LeakDetection: 1/4ContainerConstructionThickness: REGULARTypeofFuel: PRODUCTTankUsedfor: 00010000TankCapacity: 1978YearInstalled: 2ContainerNum: 002TankNum: Stock Inventor, Groundwater Monitoring Well, 10LeakDetection: 1/4ContainerConstructionThickness: UNLEADEDTypeofFuel: PRODUCTTankUsedfor: 00010000TankCapacity: 1978YearInstalled: 1ContainerNum: 001TankNum: OTAY VALLEY SHELL SVC INC (Continued) U001571104 hazardous waste at any time waste during any calendar month, and accumulates more than 1000 kg of hazardous waste at any time; or generates 100 kg or less of hazardous waste during any calendar month and accumulates less than 6000 kg of Handler: generates more than 100 and less than 1000 kg ofhazardousDescription: Small Small QuantityGeneratorClassification: 09EPARegion: NotreportedContactemail: 949-660-7545Contacttelephone: USContactcountry: CENTENNIAL, CO 80112 9201 E DRY CREEKRDContactaddress: STEVE MCHANDLERContact: CENTENNIAL, CO 80112 9201 E DRY CREEKRDMailingaddress: CAR000150185EPAID: CHULA VISTA, CA 91911 4826 AUTO PARKDRFacilityaddress: FORMER DARLING INTL OMAR RENDERINGSITEFacilityname: 01/15/2004Dateformreceivedbyagency: RCRA-SQG: 1077 ft. Site 1 of 2 in cluster G 0.204 mi. Relative: Lower Actual: 127 ft. 1/8-1/4 CHULA VISTA, CA 91911 SE CAHAZNET4826AUTOPARKDR CAR000150185 G18 RCRA-SQGFORMERDARLINGINTLOMARRENDERINGSITE 1007117610 TC5146125.2s Page 57 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 1007117610envid: HAZNET: No violationsfoundViolationStatus: Small QuantityGeneratorClassification: FORMER DARLING INTL OMAR RENDERINGSITESitename: 01/15/2004Dateformreceivedbyagency: Historical Generators: LEAD. Waste name: D008. Waste code: NoUsedoiltransporter: NoUsedoiltransferfacility: NoUsedoilSpecificationmarketer: NoUsedoilfuelmarketertoburner: NoUseroilrefiner: NoUsedoilprocessor: NoUsedoilfuelburner: NoFurnaceexemption: NoOn-site burner exemption: NoUndergroundinjectionactivity: NoTreater, storer or disposer of HW: NoTransporterofhazardouswaste: NoRecyclerofhazardouswaste: NoMixedwaste (haz. and radioactive): NoU.S. importer of hazardous waste: Handler Activities Summary: NotreportedOwner/Op end date: 08/22/2003Owner/Op start date: OwnerOwner/Operator Type: PrivateLegalstatus: NotreportedOwner/operator extension: NotreportedOwner/operator fax: NotreportedOwner/operator email: NotreportedOwner/operator telephone: USOwner/operator country: Not reported NotreportedOwner/operator address: KNOWLTON REALTY ADVISORSLLCOwner/operator name: NotreportedOwner/Op end date: 12/29/1999Owner/Op start date: OperatorOwner/Operator Type: PrivateLegalstatus: NotreportedOwner/operator extension: NotreportedOwner/operator fax: NotreportedOwner/operator email: NotreportedOwner/operator telephone: USOwner/operator country: Not reported NotreportedOwner/operator address: OTAY MESA VENTURES IILLCOwner/operator name: Owner/Operator Summary: FORMER DARLING INTL OMAR RENDERING SITE (Continued) 1007117610 TC5146125.2s Page 58 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation CAR000150185GEPAID: 2010Year: 1007117610envid: SanDiegoFacilityCounty: NotreportedMethodDecode: NotreportedCatDecode: 0.357Tons: Fuel Blending Prior To Energy Recovery At AnotherSiteDisposalMethod: Aqueous solution with total organic residues less than 10percentWasteCategory: NotreportedTSDCounty: ARD981057870TSDEPAID: NotreportedGenCounty: SAN DIEGO, CA921018517MailingCity,St,Zip: 1230 COLUMBIA ST STE1200MailingAddress: NotreportedMailingName: 9496607545Telephone: STEVECHANDLERContact: CAR000150185GEPAID: 2011Year: 1007117610envid: SanDiegoFacilityCounty: NotreportedMethodDecode: NotreportedCatDecode: 0.357Tons: Fuel Blending Prior To Energy Recovery At AnotherSiteDisposalMethod: Aqueous solution with total organic residues less than 10percentWasteCategory: NotreportedTSDCounty: ARD981057870TSDEPAID: NotreportedGenCounty: SAN DIEGO, CA921018517MailingCity,St,Zip: 1230 COLUMBIA ST STE1200MailingAddress: NotreportedMailingName: 9496607545Telephone: STEVECHANDLERContact: CAR000150185GEPAID: 2011Year: 1007117610envid: NotreportedFacilityCounty: NotreportedMethodDecode: NotreportedCatDecode: 0.336Tons: H010-H129) Or (H131-H135) Storage, Bulking, And/Or Transfer Off Site--No Treatment/ReoveryDisposalMethod: NotreportedWasteCategory: LosAngelesTSDCounty: CAD044429835TSDEPAID: SanDiegoGenCounty: SAN DIEGO, CA921018517MailingCity,St,Zip: 1230 COLUMBIA ST STE1200MailingAddress: NotreportedMailingName: 9496607545Telephone: MATTHEWCURTISContact: CAR000150185GEPAID: 2013Year: FORMER DARLING INTL OMAR RENDERING SITE (Continued)1007117610 TC5146125.2s Page 59 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 10 additional CA_HAZNET: record(s) in the EDR Site Report. Click this hyperlink while viewing on your computer to access SanDiegoFacilityCounty: NotreportedMethodDecode: NotreportedCatDecode: 3.465Tons: Fuel Blending Prior To Energy Recovery At AnotherSiteDisposalMethod: Aqueous solution with total organic residues less than 10percentWasteCategory: NotreportedTSDCounty: ARD981057870TSDEPAID: NotreportedGenCounty: SAN DIEGO, CA921018517MailingCity,St,Zip: 1230 COLUMBIA ST STE1200MailingAddress: NotreportedMailingName: 9496607545Telephone: STEVECHANDLERContact: CAR000150185GEPAID: 2010Year: 1007117610envid: SanDiegoFacilityCounty: NotreportedMethodDecode: NotreportedCatDecode: 3.465Tons: Fuel Blending Prior To Energy Recovery At AnotherSiteDisposalMethod: Aqueous solution with total organic residues less than 10percentWasteCategory: NotreportedTSDCounty: ARD981057870TSDEPAID: NotreportedGenCounty: SAN DIEGO, CA921018517MailingCity,St,Zip: 1230 COLUMBIA ST STE1200MailingAddress: NotreportedMailingName: 9496607545Telephone: STEVECHANDLERContact: FORMER DARLING INTL OMAR RENDERING SITE (Continued) 1007117610 waste during any calendar month and accumulates less than 6000 kg of Handler: generates more than 100 and less than 1000 kg ofhazardousDescription: Small Small QuantityGeneratorClassification: 09EPARegion: NotreportedContactemail: 619-656-1291Contacttelephone: USContactcountry: CHULA VISTA, CA 91911 4501 MAINSTREETContactaddress: CLINT WEASTMANContact: CAR000180380EPAID: CHULA VISTA, CA 91911 4501 MAINSTREETFacilityaddress: KIDDIE KANDIDS #00606Facilityname: 01/05/2007Dateformreceivedbyagency: RCRA-SQG: 1122 ft. Site 3 of 3 in cluster F 0.213 mi. Relative: Lower Actual: 138 ft. 1/8-1/4 CHULA VISTA, CA 91911 SW 4501 MAIN STREET CAR000180380 F19 RCRA-SQGKIDDIEKANDIDS #00606 1010313972 TC5146125.2s Page 60 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation No violationsfoundViolationStatus: SILVER. Waste name: D011. Waste code: NoUsedoiltransporter: NoUsedoiltransferfacility: NoUsedoilSpecificationmarketer: NoUsedoilfuelmarketertoburner: NoUseroilrefiner: NoUsedoilprocessor: NoUsedoilfuelburner: NoFurnaceexemption: NoOn-site burner exemption: NoUndergroundinjectionactivity: NoTreater, storer or disposer of HW: NoTransporterofhazardouswaste: NoRecyclerofhazardouswaste: NoMixedwaste (haz. and radioactive): NoU.S. importer of hazardous waste: Handler Activities Summary: NotreportedOwner/Op end date: 11/24/2006Owner/Op start date: OwnerOwner/Operator Type: PrivateLegalstatus: NotreportedOwner/operator extension: NotreportedOwner/operator fax: NotreportedOwner/operator email: NotreportedOwner/operator telephone: USOwner/operator country: WAYNE, NJ 07470 ONE GEOFFERYWAYOwner/operator address: TOYS RUSOwner/operator name: NotreportedOwner/Op end date: 11/24/2006Owner/Op start date: OperatorOwner/Operator Type: PrivateLegalstatus: NotreportedOwner/operator extension: NotreportedOwner/operator fax: NotreportedOwner/operator email: NotreportedOwner/operator telephone: USOwner/operator country: WAYNE, NJ 07470 ONE GEOFFERYWAYOwner/operator address: TOYS RUSOwner/operator name: Owner/Operator Summary: hazardous waste at any time waste during any calendar month, and accumulates more than 1000 kg of hazardous waste at any time; or generates 100 kg or less of hazardous KIDDIE KANDIDS #00606 (Continued) 1010313972 TC5146125.2s Page 61 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NoUsedoiltransporter: NoUsedoiltransferfacility: NoUsedoilSpecificationmarketer: NoUsedoilfuelmarketertoburner: NoUseroilrefiner: NoUsedoilprocessor: NoUsedoilfuelburner: NoFurnaceexemption: NoOn-site burner exemption: NoUndergroundinjectionactivity: NoTreater, storer or disposer of HW: NoTransporterofhazardouswaste: NoRecyclerofhazardouswaste: NoMixedwaste (haz. and radioactive): NoU.S. importer of hazardous waste: Handler Activities Summary: NotreportedOwner/Op end date: NotreportedOwner/Op start date: OwnerOwner/Operator Type: PrivateLegalstatus: NotreportedOwner/operator extension: NotreportedOwner/operator fax: NotreportedOwner/operator email: 619-421-3300Owner/operator telephone: NotreportedOwner/operator country: CHULA VISTA, CA 91911 580 AUTO PARKDROwner/operator address: EDMUNDWESCHEOwner/operator name: Owner/Operator Summary: hazardous waste at any time waste during any calendar month, and accumulates more than 1000 kg of hazardous waste at any time; or generates 100 kg or less of hazardous waste during any calendar month and accumulates less than 6000 kg of Handler: generates more than 100 and less than 1000 kg ofhazardousDescription: Small Small QuantityGeneratorClassification: 09EPARegion: NotreportedContactemail: 619-421-3300Contacttelephone: USContactcountry: CHULA VISTA, CA 91911 580 AUTO PARKDRContactaddress: LEROYLAUSENGContact: CAR000002618EPAID: CHULA VISTA, CA 91911 580 AUTO PARKDRFacilityaddress: PEOPLESCHEVROLETFacilityname: 10/05/1998Dateformreceivedbyagency: RCRA-SQG: CA HAZNET 1125 ft.ECHOSite2of2inclusterG 0.213 mi.FINDS Relative: Lower Actual: 124 ft. 1/8-1/4 CA San Diego Co. HMMDCHULAVISTA, CA 91911 SE CAAST580AUTOPARKDR CAR000002618 G20 RCRA-SQGPEOPLESCHEVROLET 1000985150 TC5146125.2s Page 62 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedPropertyOwnerMailingAddress: NotreportedPropertyOwnerPhone: NotreportedPropertyOwnerName: NotreportedOwnerCountry: NotreportedOwnerZipCode: NotreportedOwnerState: NotreportedOwnerMailAddress: NotreportedOwnerPhone: NotreportedOperatorPhone: NotreportedOperatorName: NotreportedMailingAddressZipCode: NotreportedMailingAddressState: NotreportedMailingAddressCity: NotreportedMailingAddress: NotreportedFax: NotreportedPhone: NotreportedBusinessName: NotreportedFacilityID: NotreportedCERSID: 2825TotalGallons: EDWESCHEOwner: SanDiegoCertifiedUnifiedProgramAgencies: AST: No violationsfoundViolationStatus: TRICHLORETHYLENE. Waste name: D040. Waste code: TETRACHLOROETHYLENE. Waste name: D039. Waste code: METHYL ETHYL KETONE. Waste name: D035. Waste code: 1,4-DICHLOROBENZENE. Waste name: D027. Waste code: CHLOROBENZENE. Waste name: D021. Waste code: BENZENE. Waste name: D018. Waste code: LEAD. Waste name: D008. Waste code: CADMIUM. Waste name: D006. Waste code: CORROSIVE WASTE. Waste name: D002. Waste code: IGNITABLE WASTE. Waste name: D001. Waste code: Not Defined. Waste name: D000. Waste code: PEOPLES CHEVROLET (Continued)1000985150 TC5146125.2s Page 63 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NTradeSecret: DEH2017-HCHEM-0131304ChildRecordId: YActivePermit: PermitRenewedPermitStatus: DEH2009-HUPFP-211063RecordID: MixtureCaseNumber: LubricatingOilsCommonName: Paraffinic PetroleumDistillatesChemicalName: 2017-02-24T00:50:21.000LastUpdated: MixtureHazardousMaterialType: NTradeSecret: DEH2017-HCHEM-0131303ChildRecordId: YActivePermit: PermitRenewedPermitStatus: DEH2009-HUPFP-211063RecordID: NotreportedCaseNumber: WasteAbsorbentCommonName: WasteAbsorbentChemicalName: 2017-02-24T00:50:21.000LastUpdated: NotreportedHazardousMaterialType: NTradeSecret: DEH2017-HWAST-0109755ChildRecordId: YActivePermit: PermitRenewedPermitStatus: DEH2009-HUPFP-211063RecordID: Waste and Materials: NotreportedGenerateMedicalWaste: NTreatHazWaste: YGenerateHazWaste: NotreportedSubjectToAPSA: NotreportedOwnOrOperateUST: NotreportedHandleRegulatedHazmat: NUSTOwner: NotreportedFacilityMailingZip: NotreportedFacilityMailingState: NotreportedFacilityMailingCity: 540 AUTO PARK DR, CHULA VISTA, CA91911FacilityMailingAddress: NotreportedFacilityOwner: 07/27/2017DateLastUpdated: NotreportedPermitExpiration: PermitRenewedPermitStatus: 619-656-7500FacilityTelephone: NotreportedLastHMMDInspection: NotreportedAPN: CAL00034298EPAIdNumber: NotreportedBusinessType: NotreportedPermitNumber: HMMD SAN DIEGO: NotreportedEPAID: NotreportedPropertyOwnerCountry: NotreportedPropertyOwnerZipCode: NotreportedPropertyOwnerStat : NotreportedPropertyOwnerCity: PEOPLES CHEVROLET (Continued)1000985150 TC5146125.2s Page 64 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 2017-02-24T00:50:21.000LastUpdated: NotreportedHazardousMaterialType: NTradeSecret: DEH2017-HWAST-0109754ChildRecordId: YActivePermit: PermitRenewedPermitStatus: DEH2009-HUPFP-211063RecordID: NotreportedCaseNumber: Waste BrakeFluidCommonName: Waste DiethyleneGlycolChemicalName: 2017-02-24T00:50:21.000LastUpdated: NotreportedHazardousMaterialType: NTradeSecret: DEH2017-HWAST-0109753ChildRecordId: YActivePermit: PermitRenewedPermitStatus: DEH2009-HUPFP-211063RecordID: NotreportedCaseNumber: WasteCoolantCommonName: Waste EthyleneGlycolChemicalName: 2017-02-24T00:50:21.000LastUpdated: NotreportedHazardousMaterialType: NTradeSecret: DEH2017-HWAST-0109752ChildRecordId: YActivePermit: PermitRenewedPermitStatus: DEH2009-HUPFP-211063RecordID: NotreportedCaseNumber: Used LubricatingOilsCommonName: Used Paraffinic PetroleumDistillatesChemicalName: 2017-02-24T00:50:21.000LastUpdated: NotreportedHazardousMaterialType: NTradeSecret: DEH2017-HWAST-0109751ChildRecordId: YActivePermit: PermitRenewedPermitStatus: DEH2009-HUPFP-211063RecordID: MixtureCaseNumber: Cleaners/SoapsCommonName: Cleaners/SoapsChemicalName: 2017-02-24T00:50:21.000LastUpdated: MixtureHazardousMaterialType: NTradeSecret: DEH2017-HCHEM-0131305ChildRecordId: YActivePermit: PermitRenewedPermitStatus: DEH2009-HUPFP-211063RecordID: MixtureCaseNumber: CoolantCommonName: EthyleneGlycolChemicalName: 2017-02-24T00:50:21.000LastUpdated: MixtureHazardousMaterialType: PEOPLES CHEVROLET (Continued)1000985150 TC5146125.2s Page 65 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation YGenerateHazWaste: NotreportedSubjectToAPSA: NotreportedOwnOrOperateUST: YHandleRegulatedHazmat: NotreportedUSTOwner: 91911FacilityMailingZip: CAFacilityMailingState: CHULAVISTAFacilityMailingCity: 580 AUTO PARKDRFacilityMailingAddress: FULLERHONDAFacilityOwner: 11/02/2012DateLastUpdated: 11/30/2013PermitExpiration: OPENPermitStatus: 619-656-7500FacilityTelephone: 03/06/2012LastHMMDInspection: 644-042-05-00APN: CAL000342981EPAIdNumber: 6HK31BusinessType: 211063PermitNumber: NotreportedCaseNumber: ClarifierSludgeCommonName: ClarifierSludgeChemicalName: 2017-02-24T00:50:21.000LastUpdated: NotreportedHazardousMaterialType: NTradeSecret: DEH2017-HWAST-0109758ChildRecordId: YActivePermit: PermitRenewedPermitStatus: DEH2009-HUPFP-211063RecordID: NotreportedCaseNumber: Parts WasherWasteCommonName: Parts WasherWasteChemicalName: 2017-02-24T00:50:21.000LastUpdated: NotreportedHazardousMaterialType: NTradeSecret: DEH2017-HWAST-0109757ChildRecordId: YActivePermit: PermitRenewedPermitStatus: DEH2009-HUPFP-211063RecordID: NotreportedCaseNumber: Waste FuelPumpsCommonName: Waste Solids with GasolineResidueChemicalName: 2017-02-24T00:50:21.000LastUpdated: NotreportedHazardousMaterialType: NTradeSecret: DEH2017-HWAST-0109756ChildRecordId: YActivePermit: PermitRenewedPermitStatus: DEH2009-HUPFP-211063RecordID: NotreportedCaseNumber: WasteFuelCommonName: Waste Gasoline/DieselChemicalName: PEOPLES CHEVROLET (Continued)1000985150 TC5146125.2s Page 66 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: ANTIFREEZE / COOLANTOtherInformation: WASTE 342 ORGANIC LIQUIDS W/METALSName: NotreportedCaseNumber: 11/02/2012UpdateDate: 211063PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: OILYABSORBENTOtherInformation: WASTE 223 UNSPEC OIL CONTAININGWASTEName: NotreportedCaseNumber: 11/02/2012UpdateDate: 211063PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: NotreportedOtherInformation: WASTE 221 WASTE OIL & MIXEDOILName: NotreportedCaseNumber: 11/02/2012UpdateDate: 211063PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: BRAKE CLEANER (3)Other Information: WASTE 214 UNSPEC SOLVENTMIXTUREName: NotreportedCaseNumber: 11/02/2012UpdateDate: 211063PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: PARTSWASHEROtherInformation: WASTE 135 UNSPECIFIED AQUEOUS SOL’NName: NotreportedCaseNumber: 11/02/2012UpdateDate: 211063PermitNumber: NotreportedHazardousCategories2: CHRONICHazardousCategories1: MaterialMaterialWaste: MOTOR, TRANSMISSION & GEAR LUBRICATINGOILSOtherInformation: PARAFFINIC PETROLEUMDISTILLATESName: NotreportedCaseNumber: 11/02/2012UpdateDate: 211063PermitNumber: Inventory Active Permits (not SQG Medical): NotreportedGenerateMedicalWaste: NotreportedTreatHazWaste: PEOPLES CHEVROLET (Continued)1000985150 TC5146125.2s Page 67 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation WASTE CONTAINER W/OLABELSViolation: 6HV0202ViolationCode: 09/12/2003InspectionDate: 11/02/2012UpdateDate: 135062PermitNumber: Violations Inactive Permits: NotreportedGenerateMedicalWaste: NotreportedTreatHazWaste: YGenerateHazWaste: NotreportedSubjectToAPSA: NotreportedOwnOrOperateUST: YHandleRegulatedHazmat: NotreportedUSTOwner: 91911-Facility Mailing Zip: CAFacilityMailingState: CHULAVISTAFacilityMailingCity: 580 AUTO PARKDRFacilityMailingAddress: EDWESCHEFacilityOwner: 11/02/2012DateLastUpdated: 11/30/2009PermitExpiration: INACPermitStatus: 619-421-3300FacilityTelephone: 09/11/2008LastHMMDInspection: 644-042-05-00APN: CAR000002618EPAIdNumber: 6HK31BusinessType: 135062PermitNumber: ACTIVEActivity: manage it within one year. 66261.7(e) & (f). Failed to mark date on empty container larger than 5 gallons and/orViolationCitation: MISMANAGED EMPTY CONTAINERS >5GALS.Violation: 6HV0224ViolationCode: 03/06/2012InspectionDate: 11/02/2012UpdateDate: 211063PermitNumber: Violations Active Permits: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: DRAINEDOtherInformation: WASTE 888 USED OILFILTERSName: NotreportedCaseNumber: 11/02/2012UpdateDate: 211063PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: INTERSTATE / USED LEAD ACIDBATTERIESOtherInformation: WASTE 444 USEDBATTERIESName: NotreportedCaseNumber: 11/02/2012UpdateDate: 211063PermitNumber: PEOPLES CHEVROLET (Continued)1000985150 TC5146125.2s Page 68 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation InactivePermitActivity: 66262.34(a)(3) & 66262.34(f) date and/or are improperly labeled. CCR 66262.34(a)(2); Hazardous waste containers &/or tanks are missing labels, accumulationViolationCitation: WASTE CONTAINER W/OLABELSViolation: 6HV0202ViolationCode: 09/12/2003InspectionDate: 11/02/2012UpdateDate: 135062PermitNumber: Violations Inactive Permits: NotreportedGenerateMedicalWaste: NotreportedTreatHazWaste: YGenerateHazWaste: NotreportedSubjectToAPSA: NotreportedOwnOrOperateUST: YHandleRegulatedHazmat: NotreportedUSTOwner: 91911-Facility Mailing Zip: CAFacilityMailingState: CHULAVISTAFacilityMailingCity: 580 AUTO PARKDRFacilityMailingAddress: EDWESCHEFacilityOwner: 11/02/2012DateLastUpdated: 11/30/2009PermitExpiration: INACPermitStatus: 619-421-3300FacilityTelephone: 09/11/2008LastHMMDInspection: 644-042-05-00APN: CAR000002618EPAIdNumber: 6HK31BusinessType: 135062PermitNumber: InactivePermitActivity: 66265.195 ( c) Failed to inspect and/or document daily HW tank system inspections. Violation Citation: NO DAILY TANK INSPECTION/LOGViolation: 6HV1605ViolationCode: 06/06/2005InspectionDate: 11/02/2012UpdateDate: 135062PermitNumber: InactivePermitActivity: 25189.5(a) or 25189(d) point (ground, storm drain, sewer system, trash, or air). HSC Disposal or causing the disposal of hazardous waste to anunauthorizedViolationCitation: HAZWASTE:UNAUTHORIZEDDISPOSALViolation: 6HV0301ViolationCode: 09/12/2003InspectionDate: 11/02/2012UpdateDate: 135062PermitNumber: InactivePermitActivity: 66262.34(a)(3) & 66262.34(f) date and/or are improperly labeled. CCR 66262.34(a)(2); Hazardous waste containers &/or tanks are missing labels, accumulationViolationCitation: PEOPLES CHEVROLET (Continued)1000985150 TC5146125.2s Page 69 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation WasteMaterialWaste: PARTSWASHEROtherInformation: WASTE 135 UNSPECIFIED AQUEOUS SOL’NName: NotreportedCaseNumber: 11/02/2012UpdateDate: 211063PermitNumber: NotreportedHazardousCategories2: CHRONICHazardousCategories1: MaterialMaterialWaste: MOTOR, TRANSMISSION & GEAR LUBRICATINGOILSOtherInformation: PARAFFINIC PETROLEUMDISTILLATESName: NotreportedCaseNumber: 11/02/2012UpdateDate: 211063PermitNumber: Inventory Active Permits (not SQG Medical): NotreportedGenerateMedicalWaste: NotreportedTreatHazWaste: YGenerateHazWaste: NotreportedSubjectToAPSA: NotreportedOwnOrOperateUST: YHandleRegulatedHazmat: NotreportedUSTOwner: 91911FacilityMailingZip: CAFacilityMailingState: CHULAVISTAFacilityMailingCity: 580 AUTO PARKDRFacilityMailingAddress: FULLERHONDAFacilityOwner: 11/02/2012DateLastUpdated: 11/30/2013PermitExpiration: OPENPermitStatus: 619-656-7500FacilityTelephone: 03/06/2012LastHMMDInspection: 644-042-05-00APN: CAL000342981EPAIdNumber: 6HK31BusinessType: 211063PermitNumber: InactivePermitActivity: 66265.195 ( c) Failed to inspect and/or document daily HW tank system inspections. Violation Citation: NO DAILY TANK INSPECTION/LOGViolation: 6HV1605ViolationCode: 06/06/2005InspectionDate: 11/02/2012UpdateDate: 135062PermitNumber: InactivePermitActivity: 25189.5(a) or 25189(d) point (ground, storm drain, sewer system, trash, or air). HSC Disposal or causing the disposal of hazardous waste to anunauthorizedViolationCitation: HAZWASTE:UNAUTHORIZEDDISPOSALViolation: 6HV0301ViolationCode: 09/12/2003InspectionDate: 11/02/2012UpdateDate: 135062PermitNumber: PEOPLES CHEVROLET (Continued)1000985150 TC5146125.2s Page 70 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: DRAINEDOtherInformation: WASTE 888 USED OILFILTERSName: NotreportedCaseNumber: 11/02/2012UpdateDate: 211063PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: INTERSTATE / USED LEAD ACIDBATTERIESOtherInformation: WASTE 444 USEDBATTERIESName: NotreportedCaseNumber: 11/02/2012UpdateDate: 211063PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: ANTIFREEZE / COOLANTOtherInformation: WASTE 342 ORGANIC LIQUIDS W/METALSName: NotreportedCaseNumber: 11/02/2012UpdateDate: 211063PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: OILYABSORBENTOtherInformation: WASTE 223 UNSPEC OIL CONTAININGWASTEName: NotreportedCaseNumber: 11/02/2012UpdateDate: 211063PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: NotreportedOtherInformation: WASTE 221 WASTE OIL & MIXEDOILName: NotreportedCaseNumber: 11/02/2012UpdateDate: 211063PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: BRAKE CLEANER (3)Other Information: WASTE 214 UNSPEC SOLVENTMIXTUREName: NotreportedCaseNumber: 11/02/2012UpdateDate: 211063PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: PEOPLES CHEVROLET (Continued)1000985150 TC5146125.2s Page 71 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation BRAKE CLEANER (3)Other Information: WASTE 214 UNSPEC SOLVENTMIXTUREName: NotreportedCaseNumber: 11/02/2012UpdateDate: 211063PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: PARTSWASHEROtherInformation: WASTE 135 UNSPECIFIED AQUEOUS SOL’NName: NotreportedCaseNumber: 11/02/2012UpdateDate: 211063PermitNumber: NotreportedHazardousCategories2: CHRONICHazardousCategories1: MaterialMaterialWaste: MOTOR, TRANSMISSION & GEAR LUBRICATINGOILSOtherInformation: PARAFFINIC PETROLEUMDISTILLATESName: NotreportedCaseNumber: 11/02/2012UpdateDate: 211063PermitNumber: Inventory Active Permits (not SQG Medical): NotreportedGenerateMedicalWaste: NotreportedTreatHazWaste: YGenerateHazWaste: NotreportedSubjectToAPSA: NotreportedOwnOrOperateUST: YHandleRegulatedHazmat: NotreportedUSTOwner: 91911FacilityMailingZip: CAFacilityMailingState: CHULAVISTAFacilityMailingCity: 580 AUTO PARKDRFacilityMailingAddress: FULLERHONDAFacilityOwner: 11/02/2012DateLastUpdated: 11/30/2013PermitExpiration: OPENPermitStatus: 619-656-7500FacilityTelephone: 03/06/2012LastHMMDInspection: 644-042-05-00APN: CAL000342981EPAIdNumber: 6HK31BusinessType: 211063PermitNumber: ACTIVEActivity: manage it within one year. 66261.7(e) & (f). Failed to mark date on empty container larger than 5 gallons and/orViolationCitation: MISMANAGED EMPTY CONTAINERS >5GALS.Violation: 6HV0224ViolationCode: 03/06/2012InspectionDate: 11/02/2012UpdateDate: 211063PermitNumber: Violations Active Permits: PEOPLES CHEVROLET (Continued)1000985150 TC5146125.2s Page 72 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation manage it within one year. 66261.7(e) & (f). Failed to mark date on empty container larger than 5 gallons and/orViolationCitation: MISMANAGED EMPTY CONTAINERS >5GALS.Violation: 6HV0224ViolationCode: 03/06/2012InspectionDate: 11/02/2012UpdateDate: 211063PermitNumber: Violations Active Permits: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: DRAINEDOtherInformation: WASTE 888 USED OILFILTERSName: NotreportedCaseNumber: 11/02/2012UpdateDate: 211063PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: INTERSTATE / USED LEAD ACIDBATTERIESOtherInformation: WASTE 444 USEDBATTERIESName: NotreportedCaseNumber: 11/02/2012UpdateDate: 211063PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: ANTIFREEZE / COOLANTOtherInformation: WASTE 342 ORGANIC LIQUIDS W/METALSName: NotreportedCaseNumber: 11/02/2012UpdateDate: 211063PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: OILYABSORBENTOtherInformation: WASTE 223 UNSPEC OIL CONTAININGWASTEName: NotreportedCaseNumber: 11/02/2012UpdateDate: 211063PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: NotreportedOtherInformation: WASTE 221 WASTE OIL & MIXEDOILName: NotreportedCaseNumber: 11/02/2012UpdateDate: 211063PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: PEOPLES CHEVROLET (Continued)1000985150 TC5146125.2s Page 73 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation CHULA VISTA, CA919110000MailingCity,St,Zip: 580 AUTO PARKDRMailingAddress: NotreportedMailingName: 6194213300Telephone: EDMUND WESCHEPRESContact: CAR000002618GEPAID: 2009Year: 1000985150envid: SanDiegoFacilityCounty: NotreportedMethodDecode: NotreportedCatDecode: 0.0375Tons: Metals Recovery Including Retoring,Smelting,Chemicals,EctDisposalMethod: Other inorganic solidwasteWasteCategory: NotreportedTSDCounty: CAD982411993TSDEPAID: NotreportedGenCounty: CHULA VISTA, CA919110000MailingCity,St,Zip: 580 AUTO PARKDRMailingAddress: NotreportedMailingName: 6194213300Telephone: EDMUND WESCHEPRESContact: CAR000002618GEPAID: 2009Year: 1000985150envid: HAZNET: http://echo.epa.gov/detailed-facility-report?fid=110002905946DFRURL: 110002905946RegistryID: 1000985150Envid: ECHO: additional FINDS: detail in the EDR Site Report. Click this hyperlink while viewing on your computer to access corrective action activities required under RCRA. program staff to track the notification, permit, compliance, and and treat, store, or dispose of hazardous waste. RCRAInfo allows RCRA events and activities related to facilities that generate, transport, Conservation and Recovery Act (RCRA) program through the tracking of RCRAInfo is a national information system that supports the Resource facilities. generators, transporters, and treatment, storage, and disposal provides California with information on hazardous waste shipments for California Hazardous Waste Tracking System - Datamart (HWTS-DATAMART) Environmental Interest/Information System 110002905946RegistryID: FINDS: ACTIVEActivity: PEOPLES CHEVROLET (Continued)1000985150 TC5146125.2s Page 74 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation TXD077603371TSDEPAID: NotreportedGenCounty: CHULA VISTA, CA919110000MailingCity,St,Zip: 580 AUTO PARKDRMailingAddress: NotreportedMailingName: 6194213300Telephone: EDMUND WESCHEPRESContact: CAR000002618GEPAID: 2009Year: 1000985150envid: SanDiegoFacilityCounty: NotreportedMethodDecode: NotreportedCatDecode: 0.075Tons: Fuel Blending Prior To Energy Recovery At AnotherSiteDisposalMethod: Oxygenated solvents (acetone, butanol, ethyl acetate, etc.)Waste Category: NotreportedTSDCounty: TXD077603371TSDEPAID: NotreportedGenCounty: CHULA VISTA, CA919110000MailingCity,St,Zip: 580 AUTO PARKDRMailingAddress: NotreportedMailingName: 6194213300Telephone: EDMUND WESCHEPRESContact: CAR000002618GEPAID: 2009Year: 1000985150envid: SanDiegoFacilityCounty: NotreportedMethodDecode: NotreportedCatDecode: 0.105Tons: Fuel Blending Prior To Energy Recovery At AnotherSiteDisposalMethod: Liquids with halogenated organic compounds >= 1,000 Mg./LWasteCategory: NotreportedTSDCounty: TXD077603371TSDEPAID: NotreportedGenCounty: CHULA VISTA, CA919110000MailingCity,St,Zip: 580 AUTO PARKDRMailingAddress: NotreportedMailingName: 6194213300Telephone: EDMUND WESCHEPRESContact: CAR000002618GEPAID: 2009Year: 1000985150envid: SanDiegoFacilityCounty: NotreportedMethodDecode: NotreportedCatDecode: 1.5456Tons: H010-H129) Or (H131-H135) Storage, Bulking, And/Or Transfer Off Site--No Treatment/ReoveryDisposalMethod: Aqueous solution with total organic residues less than 10percentWasteCategory: NotreportedTSDCounty: CAT000613893TSDEPAID: NotreportedGenCounty: PEOPLES CHEVROLET (Continued)1000985150 TC5146125.2s Page 75 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 62 additional CA_HAZNET: record(s) in the EDR Site Report. Click this hyperlink while viewing on your computer to access SanDiegoFacilityCounty: NotreportedMethodDecode: NotreportedCatDecode: 0.125Tons: Fuel Blending Prior To Energy Recovery At AnotherSiteDisposalMethod: NotreportedWasteCategory: NotreportedTSDCounty: PEOPLES CHEVROLET (Continued)1000985150 87-141, [Waste Discharge Requirements (WDRs) for the Omar Rendering the waste cell has been maintained and monitored per RWQCB Order No. Rendering Company Dumpsite in the Otay River Valley). Subsequently, with RWQCB Order No. 80-06 (Closure Requirements for the Omar capped waste cell in the northwest corner of the site, in accordance soil from beneath the Class I waste ponds was placed in a lined and and disposed at a permitted off site location. In 1981, the impacted to 1980, the contents of six former Class I waste ponds were removed from 1959 to 1978 and utilized evaporation ponds for disposal. Prior chain-link and wood fence. The facility accepted hazardous wastes The Omar Rendering site is situated on forty acres enclosed byaSiteHistory: Motor / Hydraulic / Lubricating, Other Petroleum Acids/Corrosives, Arsenic, * Chlorinated Hydrocarbons, Waste Oil /Potential Contaminants of Concern: L10003156547EDRLinkID: Aquifer used for drinking water supply, SoilPotentialMediaAffect: RegionalBoardFileLocation: H02426-003LOCCaseNumber: 2091200RBCaseNumber: NotreportedLocalAgency: SAMCaseworker: SAN DIEGO RWQCB (REGION 9)Lead Agency: 10/22/2013StatusDate: Open - Closed/withMonitoringStatus: Land DisposalSiteCaseType: 117.0246Longitude: 32.59704Latitude: L10003156547GlobalId: LDS: 12/29/1999DeedDate(s): YCovenantUploaded: SWRCBAgency: NotreportedStatus: LANDFILLSiteType: NotreportedSubArea: NotreportedArea: L10003156547EnvirostorID: DEED: CA NPDES 1325 ft.CA ENF 0.251 mi.CA Cortese Relative: Lower Actual: 178 ft. 1/4-1/2 CA BOND EXP. PLANCHULAVISTA, CA 91910 East CALDS1886AUTOPARKPLACE N/A 21 CADEEDFORMEROMARRENDERINGLANDFILL S100833528 TC5146125.2s Page 76 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation chromium, nickel, lead, 1,1-dichloroethane, cadmium, dichlorodiphenyl, solutions, and heavy metals. Soil samples indicate the presence of copper, Chemicals disposed of onsite include petroleum hydrocarbons, acids, causticHazardousWasteDesc: residues were left onsite. evaporation ponds for disposal. These ponds were excavated upon closure and the fencing. The facility accepted hazardous wastes from 1959 to 1978 and utilized This site is situated on 40 acres and is enclosed by chain link andwoodSiteDescription: will need to be established. responsible parties are unable to pay for site cleanup, another source of funds reimbursement to DHS for its oversight/monitoring costs. However, if the This site is projected to be remediated by responsible partieswithProjectRevenueSourceDesc: NotreportedProjectRevenueSourceCity,St,Zip: NotreportedProjectRevenueSourceAddr: NotreportedProjectRevenueSourceCompany: BACKLOG SITE CLEANUP PLANNINGREPORTReponsibleParty: CA BOND EXP. PLAN: Click here to access the California GeoTracker records for this facility: is not part of the cleanup being conducted under the CAO. issued under authority of Water Code section 13263, and the landfill Order 97-40 (and addenda thereto) and a detection monitoring program monitoring and maintenance of the Omar Landfill are covered by WDRs pollutants from the former waste disposal pits located onsite. The Order for cleanup and abatement of areas of the site impacted by cleanup and abatement Order R9-2003-0080 and addendum no. 1 to that compaction (Geocon, January 1982). San Diego Water Board issued waste cell contents were compacted to at least 90 percent relative content, and have low potential for generating methane gas. h The site); consequently, the material is assumed to have a low organic ponds and rendering waste ponds (pond contents were removed off primarily impacted soil excavated from beneath the former Class I dated January 1982). h The material placed in the waste cell was Geocon, Testing and Observation Services During Grading Operations, second (cm/sec), and compacted to 90 percent relative compaction determined to have a permeability of less than 1E-06 centimeters per the waste cell). h Clay material used for liners was analyzed and encountered at an elevation of 120 to 130 feet MSL in the vicinity of greater than 25 feet above the groundwater table (the water table is 155 feet mean sea level [MSL]) h The bottom of the waste cell is exposure. 53-56 ft: compacted clay liner (base is at approx. elev. of compacted soil waste There is currently no documented human health 0-6 ft: clean soil cover 6-9 ft: compacted clay cap 9-53 ft: grading plan, sheet 4 of 7, Sections A-A and B-B, dated 10-27-82). Chula Vista Engineering Department, Samual F. Savino PE, As-built area: 5 acres. h Stratigraphy, approximate depth below grade (City of cell has the following physical properties: h Approximate waste cell maintenance of the cap and surface water control features. The waste semi-annual groundwater monitoring and periodic monitoring and Monitoring and Reporting Program 97-40). Program No. 97-40 requires Cell, Omar Rendering Facility, Darling International, which includes Post-Closure Maintenance for the Class I Waste Management Containment Rendering Site 2 40 (Waste Discharge Requirements for Closure and Order No. 97-Annual/Semi-Annual Report April 2010 Former Omar No. 1 Monitoring and Reporting Program], which was replaced by RWQCB Company Closed Class I Disposal Site including Technical Change Order FORMER OMAR RENDERING LANDFILL (Continued) S100833528 TC5146125.2s Page 77 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedNAICSDesc3: NotreportedNAICSCode3: NotreportedNAICSDesc2: NotreportedNAICSCode2: NotreportedNAICSDesc1: NotreportedNAICSCode1: NotreportedSICDesc3: NotreportedSICCode3: NotreportedSICDesc2: NotreportedSICCode2: RefuseSystemsSICDesc1: 4953SICCode1: 117.02675PlaceLongitude: 32.59773PlaceLatitude: 1# Of Agencies: Privately-OwnedBusinessAgencyType: Solid Waste Class I - hazardouswastesFacilityType: LandfillPlaceSubtype: Waste ManagementUnitPlaceType: LandBankAgencyName: 245992FacilityId: 9Region: ENF: NotreportedWasteManagementUitName: NotreportedSolidWasteIdNo: 9000000215WIDId: 9Region2: 06/11/1997EffectiveDate: NotreportedWasteDischargeSystemNo: R9-1997-0040OrderNo: CORTESEFlag: NotreportedSwatR: NotreportedEnfType: NotreportedOwner: NotreportedLongitude: NotreportedLatitude: NotreportedSiteCode: NotreportedStatusDate: NotreportedCleanupStatus: NotreportedSite/Facility Type: NotreportedEnvirostorId: CORTESERegion: CORTESE: Expenditure Plans. assessment to determine a priority for scheduling the site in future Bond potential to migrate off the property. DHS will evaluate the findings of the determine the location and concentrations of contaminants onsite and the The potential responsible party conducted a site assessment in Summer, 1988toSiteActivityStatus: documented exposure at this time. occur if contaminated soils are left exposed after construction. There is no pond residuals are released from the disposal cell. Chronic exposures could compounds if soil is disturbed. Ground water contamination could occur if the The public may be exposed to contaminated dust and/or volatileorganicThreatToPublicHealth & Env: trichloroethane (TCA), aldrin, and polychlorinated biphenyls (PCBs). FORMER OMAR RENDERING LANDFILL (Continued) S100833528 TC5146125.2s Page 78 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation facility. management unit (landfill) and CAO at former Omar Rendering Post-Closure maintenance and monitoring for Class 1 waste For violations of Waste Discharge RequirementsforDescription: NOV No. R9-2013-0055, Land Bank former Omar RenderingSiteTitle: HistoricalStatus: NotreportedEPLIssuanceDate: NotreportedACLIssuanceDate: 11/30/2013TerminationDate: NotreportedAchieveDate: 04/02/2013Adoption/Issuance Date: 04/02/2013EffectiveDate: Notice ofViolationEnforcementActionType: R9-2013-0055Order / Resolution Number: 9Region: 389620EnforcementId(EID): ActiveDirection/Voice: 59 - Land Disposal Site not paying tippingfeeFeeCode: IIndividual/General: NStatusEnrollee: NotreportedWDRReview - Planned: NotreportedWDRReview - Pending: NotreportedWDRReview - No Action Required: NotreportedWDRReview - Rescind: 4/28/2005WDRReview - Revise/Renew: NotreportedWDRReview - Amend: NotreportedTerminationDate: 06/11/2005Expiration/Review Date: 06/11/1997EffectiveDate: 06/24/2013StatusDate: ActiveStatus: NotreportedApplicationFeeAmtReceived: Notreported301H: NotreportedDredgeFillFee: N - NoReclamation: NotreportedNpdesType: NotreportedMajor-Minor: NotreportedNpdes# CA#: R9-1997-0040Order #: 9Region: WDRRegMeasureType: 142900RegMeasureId: 9000000215WDID: 1# Of Programs: LNDISPProgramCategory2: LNDISPProgramCategory1: LFNONOPERProgram: NotreportedFacilityWasteType4: NotreportedFacilityWasteType3: Solid wastes, NECFacilityWasteType2: Process waste, NECFacilityWasteType: X - Facility is not aPOTWPretreatment: AComplexity: 1ThreatToWaterQuality: 0DesignFlow: RegMeasSourceOfFacility: 1# Of Places: FORMER OMAR RENDERING LANDFILL (Continued)S100833528 TC5146125.2s Page 79 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedDredgeFillFee: N - NoReclamation: NotreportedNpdesType: NotreportedMajor-Minor: NotreportedNpdes# CA#: R9-1997-0040Order #: 9Region: WDRRegMeasureType: 142900RegMeasureId: 9000000215WDID: 1# Of Programs: LNDISPProgramCategory2: LNDISPProgramCategory1: LFNONOPERProgram: NotreportedFacilityWasteType4: NotreportedFacilityWasteType3: Solid wastes, NECFacilityWasteType2: Process waste, NECFacilityWasteType: X - Facility is not aPOTWPretreatment: AComplexity: 1ThreatToWaterQuality: 0DesignFlow: RegMeasSourceOfFacility: 1# Of Places: NotreportedNAICSDesc3: NotreportedNAICSCode3: NotreportedNAICSDesc2: NotreportedNAICSCode2: NotreportedNAICSDesc1: NotreportedNAICSCode1: NotreportedSICDesc3: NotreportedSICCode3: NotreportedSICDesc2: NotreportedSICCode2: RefuseSystemsSICDesc1: 4953SICCode1: 117.02675PlaceLongitude: 32.59773PlaceLatitude: 1# Of Agencies: Privately-OwnedBusinessAgencyType: Solid Waste Class I - hazardouswastesFacilityType: LandfillPlaceSubtype: Waste ManagementUnitPlaceType: LandBankAgencyName: 245992FacilityId: 9Region: 0Total $ Paid/Completed Amount: 0Project $ Completed: 0Liability $ Paid: 0Project $ Amount: 0Liability $ Amount: 0InitialAssessedAmount: 0TotalAssessmentAmount: 1# Of Programs1: NotreportedLatestMilestoneCompletionDate: LFOPERProgram: FORMER OMAR RENDERING LANDFILL (Continued)S100833528 TC5146125.2s Page 80 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 4953SICCode1: 117.02675PlaceLongitude: 32.59773PlaceLatitude: 1# Of Agencies: Privately-OwnedBusinessAgencyType: Solid Waste Class I - hazardouswastesFacilityType: LandfillPlaceSubtype: Waste ManagementUnitPlaceType: LandBankAgencyName: 245992FacilityId: 9Region: 0Total $ Paid/Completed Amount: 0Project $ Completed: 0Liability $ Paid: 0Project $ Amount: 0Liability $ Amount: 0InitialAssessedAmount: 0TotalAssessmentAmount: 1# Of Programs1: NotreportedLatestMilestoneCompletionDate: LNDISPProgram: 8/29/03, and FS 12/30/03. Site Conceptual Model 5/30/03,Site Investigation Report of wastes at the former Omar Rendering Site. Due dates: remediation of condition of pollution from past discharges Cleanup and abatement Order for investigationandDescription: Site Order R9-2003-0080, Cleanup and Abatement Order former OmarRenderingTitle: ActiveStatus: NotreportedEPLIssuanceDate: NotreportedACLIssuanceDate: NotreportedTerminationDate: NotreportedAchieveDate: 03/27/2003Adoption/Issuance Date: 03/27/2003EffectiveDate: Clean-up and AbatementOrderEnforcementActionType: R9-2003-0080Order / Resolution Number: 9Region: 256773EnforcementId(EID): PassiveDirection/Voice: 59 - Land Disposal Site not paying tippingfeeFeeCode: IIndividual/General: NStatusEnrollee: NotreportedWDRReview - Planned: NotreportedWDRReview - Pending: NotreportedWDRReview - No Action Required: NotreportedWDRReview - Rescind: 4/28/2005WDRReview - Revise/Renew: NotreportedWDRReview - Amend: NotreportedTerminationDate: 06/11/2005Expiration/Review Date: 06/11/1997EffectiveDate: 06/24/2013StatusDate: ActiveStatus: NotreportedApplicationFeeAmtReceived: Notreported301H: FORMER OMAR RENDERING LANDFILL (Continued)S100833528 TC5146125.2s Page 81 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 06/20/2002EffectiveDate: Notice ofViolationEnforcementActionType: R9-2002-0170Order / Resolution Number: 9Region: 248056EnforcementId(EID): PassiveDirection/Voice: 59 - Land Disposal Site not paying tippingfeeFeeCode: IIndividual/General: NStatusEnrollee: NotreportedWDRReview - Planned: NotreportedWDRReview - Pending: NotreportedWDRReview - No Action Required: NotreportedWDRReview - Rescind: 4/28/2005WDRReview - Revise/Renew: NotreportedWDRReview - Amend: NotreportedTerminationDate: 06/11/2005Expiration/Review Date: 06/11/1997EffectiveDate: 06/24/2013StatusDate: ActiveStatus: NotreportedApplicationFeeAmtReceived: Notreported301H: NotreportedDredgeFillFee: N - NoReclamation: NotreportedNpdesType: NotreportedMajor-Minor: NotreportedNpdes# CA#: R9-1997-0040Order #: 9Region: WDRRegMeasureType: 142900RegMeasureId: 9000000215WDID: 1# Of Programs: LNDISPProgramCategory2: LNDISPProgramCategory1: LFNONOPERProgram: NotreportedFacilityWasteType4: NotreportedFacilityWasteType3: Solid wastes, NECFacilityWasteType2: Process waste, NECFacilityWasteType: X - Facility is not aPOTWPretreatment: AComplexity: 1ThreatToWaterQuality: 0DesignFlow: RegMeasSourceOfFacility: 1# Of Places: NotreportedNAICSDesc3: NotreportedNAICSCode3: NotreportedNAICSDesc2: NotreportedNAICSCode2: NotreportedNAICSDesc1: NotreportedNAICSCode1: NotreportedSICDesc3: NotreportedSICCode3: NotreportedSICDesc2: NotreportedSICCode2: RefuseSystemsSICDesc1: FORMER OMAR RENDERING LANDFILL (Continued)S100833528 TC5146125.2s Page 82 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 1# Of Programs: LNDISPProgramCategory2: LNDISPProgramCategory1: LFNONOPERProgram: NotreportedFacilityWasteType4: NotreportedFacilityWasteType3: Solid wastes, NECFacilityWasteType2: Process waste, NECFacilityWasteType: X - Facility is not aPOTWPretreatment: AComplexity: 1ThreatToWaterQuality: 0DesignFlow: RegMeasSourceOfFacility: 1# Of Places: NotreportedNAICSDesc3: NotreportedNAICSCode3: NotreportedNAICSDesc2: NotreportedNAICSCode2: NotreportedNAICSDesc1: NotreportedNAICSCode1: NotreportedSICDesc3: NotreportedSICCode3: NotreportedSICDesc2: NotreportedSICCode2: RefuseSystemsSICDesc1: 4953SICCode1: 117.02675PlaceLongitude: 32.59773PlaceLatitude: 1# Of Agencies: Privately-OwnedBusinessAgencyType: Solid Waste Class I - hazardouswastesFacilityType: LandfillPlaceSubtype: Waste ManagementUnitPlaceType: LandBankAgencyName: 245992FacilityId: 9Region: 0Total $ Paid/Completed Amount: 0Project $ Completed: 0Liability $ Paid: 0Project $ Amount: 0Liability $ Amount: 0InitialAssessedAmount: 0TotalAssessmentAmount: 1# Of Programs1: NotreportedLatestMilestoneCompletionDate: LFNONOPERProgram: 97-40) and M&RP 97-40. groundwater monitoring reports as required by WDR (Order Discharger failed to submit semi-annual andannualDescription: NOV Order R9-2002-0170, Failure toReportTitle: HistoricalStatus: NotreportedEPLIssuanceDate: NotreportedACLIssuanceDate: 06/20/2002TerminationDate: NotreportedAchieveDate: NotreportedAdoption/Issuance Date: FORMER OMAR RENDERING LANDFILL (Continued)S100833528 TC5146125.2s Page 83 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 9Region: 0AgencyId: ActiveFacilityStatus: CAS000002NpdesNumber: NPDES: 0Total $ Paid/Completed Amount: 0Project $ Completed: 0Liability $ Paid: 0Project $ Amount: 0Liability $ Amount: 0InitialAssessedAmount: 0TotalAssessmentAmount: 1# Of Programs1: NotreportedLatestMilestoneCompletionDate: LFNONOPERProgram: requirements and CAO R9-2003-080 see reg meas. 256773 SITE CORRECTIVE ACTION ORDER replaced byclosureDescription: Enforcement - 9000000215Title: HistoricalStatus: NotreportedEPLIssuanceDate: NotreportedACLIssuanceDate: NotreportedTerminationDate: NotreportedAchieveDate: NotreportedAdoption/Issuance Date: 06/05/1995EffectiveDate: Clean-up and AbatementOrderEnforcementActionType: LT950605Order / Resolution Number: 9Region: 221498EnforcementId(EID): PassiveDirection/Voice: 59 - Land Disposal Site not paying tippingfeeFeeCode: IIndividual/General: NStatusEnrollee: NotreportedWDRReview - Planned: NotreportedWDRReview - Pending: NotreportedWDRReview - No Action Required: NotreportedWDRReview - Rescind: 4/28/2005WDRReview - Revise/Renew: NotreportedWDRReview - Amend: NotreportedTerminationDate: 06/11/2005Expiration/Review Date: 06/11/1997EffectiveDate: 06/24/2013StatusDate: ActiveStatus: NotreportedApplicationFeeAmtReceived: Notreported301H: NotreportedDredgeFillFee: N - NoReclamation: NotreportedNpdesType: NotreportedMajor-Minor: NotreportedNpdes# CA#: R9-1997-0040Order #: 9Region: WDRRegMeasureType: 142900RegMeasureId: 9000000215WDID: FORMER OMAR RENDERING LANDFILL (Continued)S100833528 TC5146125.2s Page 84 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedCONSTYPEOTHERIND: NotreportedCONSTYPEOTHERDESRIPTION: NotreportedCONSTYPEINDUSTRIALIND: NotreportedCONSTYPEGASLINEIND: NotreportedCONSTYPEELECTRICALLINEIND: NotreportedCONSTYPECOMMERTIALIND: NotreportedCONSTYPECOMMLINEIND: NotreportedCONSTYPECABLELINEIND: NotreportedCONSTYPEBELOWGROUNDIND: NotreportedCONSTYPEABOVEGROUNDIND: NotreportedEMERGENCYPHONEEXT: NotreportedEMERGENCYPHONENO: NotreportedCONSTYPELINEARUTILITYIND: NotreportedDEVELOPERCONTACTTITLE: NotreportedDEVELOPERCONTACTNAME: NotreportedDEVELOPERZIP: NotreportedDEVELOPERSTATE: NotreportedDEVELOPERCITY: NotreportedDEVELOPERADDRESS: NotreportedDEVELOPERNAME: NotreportedOPERATORTYPE: NotreportedOPERATORCONTACTEMAIL: NotreportedOPERATORCONTACTPHONEEXT: NotreportedOPERATORCONTACTPHONE: NotreportedOPERATORCONTACTTITLE: NotreportedOPERATORCONTACTNAME: NotreportedOPERATORZIP: NotreportedOPERATORSTATE: NotreportedOPERATORCITY: NotreportedOPERATORADDRESS: NotreportedOPERATORNAME: NotreportedFACILITYCONTACTEMAIL: NotreportedFACILITYCONTACTPHONEEXT: NotreportedFACILITYCONTACTPHONE: NotreportedFACILITYCONTACTTITLE: NotreportedFACILITYCONTACTNAME: NotreportedPLACESIZEUNIT: NotreportedPLACESIZE: NotreportedSTATUSDATE: NotreportedSTATUSCODENAME: NotreportedPROCESSEDDATE: NotreportedRECEIVEDDATE: 92029DischargeZip: CaliforniaDischargeState: EncondidoDischargeCity: 1546 Auto ParkWayDischargeAddress: 160 Calle MagdalenaLLCDischargeName: NotreportedTerminationDateOfRegulatoryMeasure: NotreportedExpirationDateOfRegulatoryMeasure: 10/01/2013EffectiveDateOfRegulatoryMeasure: NotreportedAdoptionDateOfRegulatoryMeasure: ConstructionProgramType: 937C367857WDID: NotreportedPlaceId: EnrolleeRegulatoryMeasureType: 2009-0009-DWQOrderNo: 441247RegulatoryMeasureId: FORMER OMAR RENDERING LANDFILL (Continued)S100833528 TC5146125.2s Page 85 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedDEVELOPERNAME: NotreportedOPERATORTYPE: NotreportedOPERATORCONTACTEMAIL: NotreportedOPERATORCONTACTPHONEEXT: NotreportedOPERATORCONTACTPHONE: NotreportedOPERATORCONTACTTITLE: NotreportedOPERATORCONTACTNAME: NotreportedOPERATORZIP: NotreportedOPERATORSTATE: NotreportedOPERATORCITY: NotreportedOPERATORADDRESS: NotreportedOPERATORNAME: NotreportedFACILITYCONTACTEMAIL: NotreportedFACILITYCONTACTPHONEEXT: NotreportedFACILITYCONTACTPHONE: NotreportedFACILITYCONTACTTITLE: NotreportedFACILITYCONTACTNAME: NotreportedPLACESIZEUNIT: NotreportedPLACESIZE: NotreportedSTATUSDATE: NotreportedSTATUSCODENAME: NotreportedPROCESSEDDATE: NotreportedRECEIVEDDATE: 80111DischargeZip: ColoradoDischargeState: GreenwoodVillageDischargeCity: 6380 S Fiddlers GreenCircleDischargeAddress: Otay Mesa Ventures IILLCDischargeName: NotreportedTerminationDateOfRegulatoryMeasure: NotreportedExpirationDateOfRegulatoryMeasure: 05/25/2000EffectiveDateOfRegulatoryMeasure: NotreportedAdoptionDateOfRegulatoryMeasure: IndustrialProgramType: 937I015817WDID: NotreportedPlaceId: EnrolleeRegulatoryMeasureType: 97-03-DWQOrderNo: 218742RegulatoryMeasureId: 9Region: 0AgencyId: ActiveFacilityStatus: CAS000001NpdesNumber: NotreportedTERTIARYSIC: NotreportedSECONDARYSIC: NotreportedPRIMARYSIC: NotreportedCERTIFICATIONDATE: NotreportedCERTIFIERTITLE: NotreportedCERTIFIERNAME: NotreportedRECEIVINGWATERNAME: NotreportedDIRDISCHARGEUSWATERIND: NotreportedCONSTYPEWATERSEWERIND: NotreportedCONSTYPEUTILITYIND: NotreportedCONSTYPEUTILITYDESCRIPTION: NotreportedCONSTYPETRANSPORTIND: NotreportedCONSTYPERESIDENTIALIND: NotreportedCONSTYPERECONSIND: FORMER OMAR RENDERING LANDFILL (Continued)S100833528 TC5146125.2s Page 86 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 10/01/2013STATUSDATE: ActiveSTATUSCODENAME: 10/01/2013PROCESSEDDATE: 09/25/2013RECEIVEDDATE: NotreportedDischargeZip: NotreportedDischargeState: NotreportedDischargeCity: NotreportedDischargeAddress: NotreportedDischargeName: NotreportedTerminationDateOfRegulatoryMeasure: NotreportedExpirationDateOfRegulatoryMeasure: NotreportedEffectiveDateOfRegulatoryMeasure: NotreportedAdoptionDateOfRegulatoryMeasure: NotreportedProgramType: 937C367857WDID: NotreportedPlaceId: ConstructionRegulatoryMeasureType: NotreportedOrderNo: 441247RegulatoryMeasureId: 9Region: NotreportedAgencyId: NotreportedFacilityStatus: NotreportedNpdesNumber: NotreportedTERTIARYSIC: NotreportedSECONDARYSIC: NotreportedPRIMARYSIC: NotreportedCERTIFICATIONDATE: NotreportedCERTIFIERTITLE: NotreportedCERTIFIERNAME: NotreportedRECEIVINGWATERNAME: NotreportedDIRDISCHARGEUSWATERIND: NotreportedCONSTYPEWATERSEWERIND: NotreportedCONSTYPEUTILITYIND: NotreportedCONSTYPEUTILITYDESCRIPTION: NotreportedCONSTYPETRANSPORTIND: NotreportedCONSTYPERESIDENTIALIND: NotreportedCONSTYPERECONSIND: NotreportedCONSTYPEOTHERIND: NotreportedCONSTYPEOTHERDESRIPTION: NotreportedCONSTYPEINDUSTRIALIND: NotreportedCONSTYPEGASLINEIND: NotreportedCONSTYPEELECTRICALLINEIND: NotreportedCONSTYPECOMMERTIALIND: NotreportedCONSTYPECOMMLINEIND: NotreportedCONSTYPECABLELINEIND: NotreportedCONSTYPEBELOWGROUNDIND: NotreportedCONSTYPEABOVEGROUNDIND: NotreportedEMERGENCYPHONEEXT: NotreportedEMERGENCYPHONENO: NotreportedCONSTYPELINEARUTILITYIND: NotreportedDEVELOPERCONTACTTITLE: NotreportedDEVELOPERCONTACTNAME: NotreportedDEVELOPERZIP: NotreportedDEVELOPERSTATE: NotreportedDEVELOPERCITY: NotreportedDEVELOPERADDRESS: FORMER OMAR RENDERING LANDFILL (Continued)S100833528 TC5146125.2s Page 87 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 9Region: NotreportedAgencyId: NotreportedFacilityStatus: NotreportedNpdesNumber: NotreportedTERTIARYSIC: NotreportedSECONDARYSIC: NotreportedPRIMARYSIC: 25-SEP-13CERTIFICATIONDATE: CFOCERTIFIERTITLE: JohnEppsCERTIFIERNAME: OtayRiverRECEIVINGWATERNAME: YDIRDISCHARGEUSWATERIND: NCONSTYPEWATERSEWERIND: NCONSTYPEUTILITYIND: NotreportedCONSTYPEUTILITYDESCRIPTION: NCONSTYPETRANSPORTIND: NCONSTYPERESIDENTIALIND: NCONSTYPERECONSIND: NCONSTYPEOTHERIND: NotreportedCONSTYPEOTHERDESRIPTION: NCONSTYPEINDUSTRIALIND: NCONSTYPEGASLINEIND: NCONSTYPEELECTRICALLINEIND: YCONSTYPECOMMERTIALIND: NCONSTYPECOMMLINEIND: NCONSTYPECABLELINEIND: NCONSTYPEBELOWGROUNDIND: NCONSTYPEABOVEGROUNDIND: NotreportedEMERGENCYPHONEEXT: 760-522-7490EMERGENCYPHONENO: NCONSTYPELINEARUTILITYIND: SecretaryDEVELOPERCONTACTTITLE: JohnEppsDEVELOPERCONTACTNAME: 92029DEVELOPERZIP: CaliforniaDEVELOPERSTATE: EncondidoDEVELOPERCITY: 1546 Auto ParkWayDEVELOPERADDRESS: 160 Calle MagdalenaLLCDEVELOPERNAME: PrivateBusinessOPERATORTYPE: JWE@mossy.comOPERATORCONTACTEMAIL: NotreportedOPERATORCONTACTPHONEEXT: 858-581-7942OPERATORCONTACTPHONE: SecretaryOPERATORCONTACTTITLE: JohnEppsOPERATORCONTACTNAME: 92029OPERATORZIP: CaliforniaOPERATORSTATE: EncondidoOPERATORCITY: 1546 Auto ParkWayOPERATORADDRESS: 160 Calle MagdalenaLLCOPERATORNAME: lletts@lusardi.comFACILITYCONTACTEMAIL: NotreportedFACILITYCONTACTPHONEEXT: 760-744-3133FACILITYCONTACTPHONE: NotreportedFACILITYCONTACTTITLE: LarryLettFACILITYCONTACTNAME: AcresPLACESIZEUNIT: 5.1PLACESIZE: FORMER OMAR RENDERING LANDFILL (Continued)S100833528 TC5146125.2s Page 88 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedCONSTYPEOTHERIND: NotreportedCONSTYPEOTHERDESRIPTION: NotreportedCONSTYPEINDUSTRIALIND: NotreportedCONSTYPEGASLINEIND: NotreportedCONSTYPEELECTRICALLINEIND: NotreportedCONSTYPECOMMERTIALIND: NotreportedCONSTYPECOMMLINEIND: NotreportedCONSTYPECABLELINEIND: NotreportedCONSTYPEBELOWGROUNDIND: NotreportedCONSTYPEABOVEGROUNDIND: NotreportedEMERGENCYPHONEEXT: NotreportedEMERGENCYPHONENO: NotreportedCONSTYPELINEARUTILITYIND: NotreportedDEVELOPERCONTACTTITLE: NotreportedDEVELOPERCONTACTNAME: NotreportedDEVELOPERZIP: ColoradoDEVELOPERSTATE: NotreportedDEVELOPERCITY: NotreportedDEVELOPERADDRESS: NotreportedDEVELOPERNAME: PrivateBusinessOPERATORTYPE: timothy.roberts@aptim.comOPERATORCONTACTEMAIL: NotreportedOPERATORCONTACTPHONEEXT: 720-554-8206OPERATORCONTACTPHONE: NotreportedOPERATORCONTACTTITLE: TIMOTHYROBERTSOPERATORCONTACTNAME: 80111OPERATORZIP: ColoradoOPERATORSTATE: GreenwoodVillageOPERATORCITY: 6380 S Fiddlers GreenCircleOPERATORADDRESS: Otay Mesa Ventures IILLCOPERATORNAME: mark.unruh@aptim.comFACILITYCONTACTEMAIL: NotreportedFACILITYCONTACTPHONEEXT: 619-533-7301FACILITYCONTACTPHONE: ProjectManagerFACILITYCONTACTTITLE: MarkUnruhFACILITYCONTACTNAME: AcresPLACESIZEUNIT: 5PLACESIZE: 05/25/2000STATUSDATE: ActiveSTATUSCODENAME: 05/25/2000PROCESSEDDATE: 05/09/2008RECEIVEDDATE: NotreportedDischargeZip: NotreportedDischargeState: NotreportedDischargeCity: NotreportedDischargeAddress: NotreportedDischargeName: NotreportedTerminationDateOfRegulatoryMeasure: NotreportedExpirationDateOfRegulatoryMeasure: NotreportedEffectiveDateOfRegulatoryMeasure: NotreportedAdoptionDateOfRegulatoryMeasure: NotreportedProgramType: 937I015817WDID: NotreportedPlaceId: IndustrialRegulatoryMeasureType: NotreportedOrderNo: 218742RegulatoryMeasureId: FORMER OMAR RENDERING LANDFILL (Continued)S100833528 TC5146125.2s Page 89 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedTERTIARYSIC: NotreportedSECONDARYSIC: 4953-RefuseSystemsPRIMARYSIC: 10-AUG-15CERTIFICATIONDATE: ProjectManagerCERTIFIERTITLE: TIMOTHYROBERTSCERTIFIERNAME: OtayRiverRECEIVINGWATERNAME: NDIRDISCHARGEUSWATERIND: NotreportedCONSTYPEWATERSEWERIND: NotreportedCONSTYPEUTILITYIND: NotreportedCONSTYPEUTILITYDESCRIPTION: NotreportedCONSTYPETRANSPORTIND: NotreportedCONSTYPERESIDENTIALIND: NotreportedCONSTYPERECONSIND: FORMER OMAR RENDERING LANDFILL (Continued) S100833528 NotreportedRemainingCapacitywithUnits: NotreportedRemainingCapacity: NotreportedPermittedCapacitywithUnits: NotreportedActualThroughputwithUnits: NotreportedPermittedThroughputwithUnits: NotreportedProgramType: NotreportedWasteDischargeRequirementNum: 37-CR-0075SWISNum: 0.00DisposalAcreage: NotreportedClosureType: NotreportedClosureDate: NotreportedAcceptedWaste: QuarterlyInspectionFrequency: 01UnitNumber: DisposalCategory: GPSGISSource: Open Space - Irrigated,CommercialLanduseName: Pre-regulationsRegulationStatus: Solid Waste DisposalSiteActivity: 0.00PermittedAcreage: NotreportedPermitStatus: NotreportedPermitDate: NotreportedOperatorCity,St,Zip: NotreportedOperatorAddress2: NotreportedOperatorAddress: NotreportedOperatorPhone: NotreportedOperator: ClosedOperationalStatus: Chula Vista, CA91910OwnerCity,St,Zip: 276 FourthAvenueOwnerAddress2: DevelopmentServicesOwnerAddress: 6194765341OwnerTelephone: City of ChulaVistaOwnerName: 32.5916 / -117.0313Lat/Long: 37-CR-0075FacilityID: STATERegion: SWF/LF (SWIS): 1735 ft. 0.329 mi. Relative: Lower Actual: 87 ft. 1/4-1/2 CHULA VISTA, CA South S OF 4700 BLK. MAIN ST. N/A 22 CA SWF/LFSHINOHARAIIPROPERTYBURNSITE S105548884 TC5146125.2s Page 90 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 32.5916 / -117.0313Lat/Long: NotreportedRemainingCapacitywithUnits: NotreportedRemainingCapacity: NotreportedPermittedCapacitywithUnits: NotreportedActualThroughputwithUnits: NotreportedPermittedThroughputwithUnits: NotreportedProgramType: NotreportedWasteDischargeRequirementNum: 37-CR-0075SWISNum: 0.00DisposalAcreage: NotreportedClosureType: NotreportedClosureDate: NotreportedAcceptedWaste: QuarterlyInspectionFrequency: 01UnitNumber: DisposalCategory: GPSGISSource: Open Space - Irrigated,CommercialLanduseName: Pre-regulationsRegulationStatus: Solid Waste DisposalSiteActivity: 0.00PermittedAcreage: NotreportedPermitStatus: NotreportedPermitDate: NotreportedOperatorCity,St,Zip: NotreportedOperatorAddress2: NotreportedOperatorAddress: NotreportedOperatorPhone: NotreportedOperator: ClosedOperationalStatus: ChulaVistaOwnerCity,St,Zip: 2009 ChardonnayTerraceOwnerAddress2: NotreportedOwnerAddress: NotreportedOwnerTelephone: ShinoharaJOwnerName: 32.5916 / -117.0313Lat/Long: 37-CR-0075FacilityID: STATERegion: 32.5916 / -117.0313Lat/Long: SHINOHARA II PROPERTY BURNSITE (Continued) S105548884 NotreportedLocalAgency: NotreportedRBCaseNumber: NotreportedCaseWorker: 04/29/2008StatusDate: Completed - CaseClosedStatus: 117.0381Longitude: 32.5945Latitude: T0607313861GlobalId: http://geotracker.waterboards.ca.gov/profile_report.asp?global_id=T0607313861GeoTrack: LUST CleanupSiteCaseType: SAN DIEGO COUNTYLOPLeadAgency: LUST: 1914 ft. 0.363 mi. Relative: Lower Actual: 133 ft. 1/4-1/2 CHULA VISTA, CA 91911 WSW 4430 OTAY VALLEY RD N/A 23 CALUSTARCO S103980466 TC5146125.2s Page 91 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 06/25/2002StatusDate: Open - Case BeginDateStatus: T0607313861GlobalId: 04/29/2008StatusDate: Completed - CaseClosedStatus: T0607313861GlobalId: LUST: LeakBeganAction: 06/25/2002Date: OtherActionType: T0607313861GlobalId: LeakStoppedAction: 06/25/2002Date: OtherActionType: T0607313861GlobalId: LeakDiscoveryAction: 06/25/2002Date: OtherActionType: T0607313861GlobalId: CorrespondenceAction: 01/09/2007Date: RESPONSEActionType: T0607313861GlobalId: LeakReportedAction: 07/11/2002Date: OtherActionType: T0607313861GlobalId: Notice ofResponsibilityAction: 07/23/2002Date: ENFORCEMENTActionType: T0607313861GlobalId: LUST: NotreportedSiteHistory: DieselPotentialContaminantsofConcern: SoilPotentialMediaAffect: H21459-001LocalCaseNumber: LocalAgencyFileLocation: ARCO (Continued)S103980466 NotreportedSiteCode: 08/21/1995StatusDate: Refer: OtherAgencyStatus: 37730292FacilityID: ENVIROSTOR: 2016 ft.CA HISTUSTSite1of2inclusterH 0.382 mi.CA SWEEPS UST Relative: Lower Actual: 140 ft. 1/4-1/2 CA San Diego Co. HMMDCHULAVISTA, CA 92011 ESE CASLIC4501OTAYVALLEYROAD N/A H24 CAENVIROSTORVINCENTDAVIESPROPERTY U001571103 TC5146125.2s Page 92 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedRBCaseNumber: NotreportedLocalAgency: NotreportedCaseWorker: Cleanup ProgramSiteCaseType: 117.042898Longitude: 32.594208Latitude: H28262-001LeadAgencyCaseNumber: SAN DIEGO COUNTYLOPLeadAgency: T0608113999GlobalId: 05/30/1996StatusDate: Completed - CaseClosedFacilityStatus: STATERegion: SLIC: NotreportedScheduleRevisedDate: NotreportedScheduleDueDate: NotreportedScheduleDocumentType: NotreportedScheduleSubAreaName: NotreportedScheduleAreaName: NotreportedFutureDueDate: NotreportedFutureDocumentType: NotreportedFutureSubAreaName: NotreportedFutureAreaName: CalSites Validation Program confirms NFA for DTSC.Comments: 10/25/1994CompletedDate: SiteScreeningCompletedDocumentType: NotreportedCompletedSubAreaName: PROJECTWIDECompletedAreaName: Completed Info: Envirostor IDNumberAliasType: 37730292AliasName: EPA IdentificationNumberAliasType: CAD983566779AliasName: NONESPECIFIEDPotentialDescription: NONESPECIFIEDConfirmedCOC: NONESPECIFIEDPotentialCOC: NONESPECIFIEDPastUse: NONESPECIFIEDAPN: 117.0227Longitude: 32.59472Latitude: NotreportedFunding: NONESPECIFIEDSiteMgmtReq: NORestrictedUse: NotreportedSpecialProgram: 40Senate: 79Assembly: CleanupCypressDivisionBranch: MmonroySupervisor: NotreportedProgramManager: NONESPECIFIEDLeadAgency: NONESPECIFIEDRegulatoryAgencies: NONPL: NotreportedAcres: HistoricalSiteTypeDetailed: HistoricalSiteType: VINCENT DAVIES PROPERTY (Continued)U001571103 TC5146125.2s Page 93 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 02-29-88CreatedDate: 06-26-92ActionDate: NotreportedReferralDate: 44-022391BoardOfEqualization: 9Number: 6804CompNumber: ActiveStatus: SWEEPS UST: ALTERNATIVE DURING INSPECTION. NO MONITORING ALTERNATIVE SELECTED. VERIFY AND ENTERMONITORINGUSTMonitorMethod: 90MonitorCode: GRAVITYDeliverySystem: NotreportedPipeType: 1968-01-01 00:00:00YearInstalled: NotreportedRemoveCloseDate: EXEMPTRegStatus: LEADEDOtherContentInfo: LEADEDUSTContents: 300CapacityGallons: 1AdditionalId: SINGLEWALLTankType: 106804PermitNumber: 2012-11-02 14:17:38LastUpdate: UNDERGROUND TANK 106804T001USTName: UST: NotreportedGenerateMedicalWaste: NotreportedTreatHazWaste: NotreportedGenerateHazWaste: NotreportedSubjectToAPSA: NotreportedOwnOrOperateUST: NotreportedHandleRegulatedHazmat: NAKANOFARMSUSTOwner: 92053-Facility Mailing Zip: CAFacilityMailingState: NESTORFacilityMailingCity: P.O. BOX P O BOX57FacilityMailingAddress: NAKANOFARMSFacilityOwner: 11/02/2012DateLastUpdated: NotreportedPermitExpiration: INACPermitStatus: 619-421-6581FacilityTelephone: NotreportedLastHMMDInspection: DEH-106804APN: NotreportedEPAIdNumber: 6HK03BusinessType: 106804PermitNumber: HMMD SAN DIEGO: Click here to access the California GeoTracker records for this facility: NotreportedSiteHistory: NotreportedPotentialContaminantsofConcern: NotreportedPotentialMediaAffected: LocalAgencyFileLocation: VINCENT DAVIES PROPERTY (Continued) U001571103 TC5146125.2s Page 94 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation Click here for Geo Tracker PDF: NoneLeakDetection: 1/4ContainerConstructionThickness: REGULARTypeofFuel: PRODUCTTankUsedfor: 00000300TankCapacity: 1968YearInstalled: 1ContainerNum: 001TankNum: 0001TotalTanks: CHULA VISTA, CA92011OwnerCity,St,Zip: 4501 OTAY VALLEYROADOwnerAddress: NAKANOFARMSOwnerName: 6194216581Telephone: NotreportedContactName: FARMOtherType: OtherFacilityType: 00000050131FacilityID: STATERegion: http://geotracker.waterboards.ca.gov/ustpdfs/pdf/0002F086.pdfURL: 0002F086FileNumber: HIST UST: 1NumberOfTanks: LEADEDContent: PSTG: M.V. FUELTankUse: NotreportedActiveDate: 300Capacity: ATankStatus: 37-000-006804-000001SWRCBTankId: NotreportedOwnerTankId: VINCENT DAVIES PROPERTY (Continued) U001571103 13003854.00000PersonID: 13289422.00000ContactSequenceID: CERCLIS-NFRAP Site Contact Details: NFRAP-Site does not qualify for the NPL based on existinginformationNonNPLStatus: Not on theNPLNPLStatus: Not a FederalFacilityFederalFacility: 0900023SiteID: Following information was gathered from the prior CERCLIS update completed in 10/2013: NFRAP-Site does not qualify for the NPL based on existinginformationNonNPLStatus: Not on theNPLNPL: NFederalFacility: CAD983566779EPAID: 900023SiteID: SEMS-ARCHIVE: 2016 ft. Site 2 of 2 in cluster H 0.382 mi. Relative: Lower Actual: 140 ft. 1/4-1/2 CHULA VISTA, CA 92011 ESE 4501 OTAY VALLEY ROAD CAD983566779 H25 SEMS-ARCHIVEVINCENTDAVIESPROPERTY 1003877949 TC5146125.2s Page 95 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NFRAP-Site does not qualify for the NPL based on existinginformationPriorityLevel: 01/27/92DateCompleted: Date Started: PRELIMINARYASSESSMENTAction: NotreportedPriorityLevel: 01/27/92DateCompleted: Date Started: ARCHIVESITEAction: NotreportedPriorityLevel: 08/24/90DateCompleted: Date Started: DISCOVERYAction: CERCLIS-NFRAP Assessment History: 13004003.00000PersonID: 13300875.00000ContactSequenceID: 13003858.00000PersonID: 13295017.00000ContactSequenceID: VINCENT DAVIES PROPERTY (Continued) 1003877949 NotreportedCleanupFundingEntity: NotreportedAssessmentFundingEntity: NotreportedRedevelopmentStartDate: NotreportedRedev. Funding Entity Name: NotreportedRedev. Funding Source: NotreportedRedevelopmentFunding: US EPA - Brownfields Assessment CooperativeAgreementAssessmentFundingSource: 4186AssessmentFunding: NotreportedCleanupFundingSource: NotreportedCleanupFunding: NotreportedAcresCleanedUp: NotreportedCompletedDate: NotreportedRedevCompletitionDate: NotreportedStartDate: NotreportedICDataAccess: 109352AcresPropertyID: World Geodetic System of1984Datum: NotreportedHighlights: Center of a Facility orStationPointofReference: NotreportedMapScale: Interpolation-OtherHCMLabel: 117.03442Longitude: 32.59085Latitude: 8.61Parcelsize: 624-071-01PropertyNumber: AssessmentGrantType: Chula Vista RedevelopmentAgencyRecipientName: DAVIESPROPERTYPropertyName: US BROWNFIELDS: 2112 ft. 0.400 mi. Relative: Lower Actual: 81 ft. 1/4-1/2 CHULA VISTA, CA 91911 SSW NO ADDRESS N/A 26 USBROWNFIELDSDAVIESPROPERTY 1016356769 TC5146125.2s Page 96 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedPastusegreenspaceacreage: NotreportedNum. of cleanup and re-dev. jobs: NotreportedCleanupotherdescription: NotreportedVOCscleaned: NotreportedVOCsfound: NotreportedSurfacewatercleaned: NotreportedSoilcleanedup: NotreportedSoilaffected: NotreportedSedimentscleaned: NotreportedSedimentsfound: NotreportedPetroproductscleaned: NotreportedPetroproductsfound: NotreportedPCBscleanedup: NotreportedPCBsfound: NotreportedPAHscleanedup: NotreportedPAHsfound: NotreportedOthercontamsfounddescription: NotreportedOthercontaminantsfound: NotreportedOthermetalscleaned: NotreportedOthermetalsfound: NotreportedOthercleanedup: NotreportedUnknownmediaaffected: NotreportedNomediaaffected: NotreportedLeadcleanedup: NotreportedLeadcontaminantfound: NotreportedGroundwatercleaned: NotreportedGroundwateraffected: NotreportedDrinkingwatercleaned: NotreportedDrinkingwateraffected: NotreportedControledsubstancecleaned: NotreportedControledsubstancefound: NotreportedAsbestoscleaned: NotreportedAsbestosfound: NotreportedAircleaned: NotreportedAircontaminated: NotreportedState/tribal NFA date: NotreportedState/tribal program ID: NotreportedState/tribal program date: NotreportedICinplace: NotreportedICinplacedate: NotreportedICCat. Enforcement Permit Tools: NotreportedICCat. Gov. Controls: NotreportedICCat. Info. Devices: NotreportedICCategoryProprietaryControls: UInstitutionalControlsRequired: NotreportedPhotoAvailable: NVideoAvailable: UCleanupRequired: NotreportedDidOwnerChange: City of ChulaVistaCurrentOwner: 10/24/2009 00:00:00CompletionDate: GovernmentOwnershipEntity: 09/01/2009 00:00:00StartDate: 96943301CooperativeAgreementNumber: 1AccomplishmentCount: Phase I EnvironmentalAssessmentAccomplishmentType: HazardousGrantType: DAVIES PROPERTY (Continued)1016356769 TC5146125.2s Page 97 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 17.5%Unemployed Percent: 235UnemployedNumber: 72.3%Vacant Housing Percent: 57VacantHousingNumber: 3.7%Meidan Income Percent: 1106MeidanIncomeNumber: 1181MeidanIncome: 22.6%Below Poverty Percent: 182BelowPovertyNumber: 2005- present Agricultural Uses dairy farm 1928-1967 Open Storage 1967-2004VacantPropertyDescription: NotreportedPastUse: Multistory NotreportedUnknownmediacleanedup: NotreportedIndoorairmediacleanedup: NotreportedBuildingmaterialmediacleanedup: NotreportedMediaaffectedindoorair: NotreportedMediaaffectedBluidingMaterial: NotreportedFutureUse: Multistory NotreportedUnknowncontaminantfound: NotreportedSVOCscontaminantfound: NotreportedSeleniumcontaminantfound: NotreportedPesticidescontaminantfound: NotreportedNocontaminantfound: NotreportedNickelcontaminantfound: NotreportedMercurycontaminantfound: NotreportedIroncontaminantfound: NotreportedCoppercontaminantfound: NotreportedChromiumcontaminantfound: NotreportedCadmiumcontaminantfound: NotreportedArseniccontaminantfound: NotreportedUnknowncleanup: NotreportedSVOCscleanedup: NotreportedSeleniumcleanedup: NotreportedPesticidescleanedup: NotreportedNocleanup: NotreportedNickelCleanedUp: Notreportedmercurycleanedup: NotreportedIroncleanedup: NotreportedCoppercleanedup: NotreportedChromiumcleanedup: NotreportedCadmiumcleanedup: NotreportedArseniccleanedup: NotreportedSuperfundFed. landowner flag: NotreportedGreenspaceacreageandtype: NotreportedFutureuseindustrialacreage: NotreportedFutureusecommercialacreage: NotreportedFutureuseresidentialacreage: NotreportedFutureusegreenspaceacreage: 8.61Pastuseindustrialacreage: NotreportedPastusecommercialacreage: NotreportedSurfaceWater: NotreportedPastuseresidentialacreage: DAVIES PROPERTY (Continued)1016356769 TC5146125.2s Page 98 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation Preliminary AssessmentReportCompletedDocumentType: NotreportedCompletedSubAreaName: PROJECTWIDECompletedAreaName: SITE SCREENING DONE PENDING: RWQCB LEAD. RWQCB SITE REFERRED TO SAN DIEGO RWQCB. DELISTED FROM BEP BACKLOG.Comments: 08/27/1990CompletedDate: SiteScreeningCompletedDocumentType: NotreportedCompletedSubAreaName: PROJECTWIDECompletedAreaName: FACILITY IDENTIFIED VIA ROUTINESURVEILLANCEComments: 01/13/1983CompletedDate: DiscoveryCompletedDocumentType: NotreportedCompletedSubAreaName: PROJECTWIDECompletedAreaName: Completed Info: Envirostor IDNumberAliasType: 37500032AliasName: Project Code (Site Code)Alias Type: 400004AliasName: PCodeAliasType: P43063AliasName: EPA IdentificationNumberAliasType: CAD980515860AliasName: NONESPECIFIEDPotentialDescription: NONESPECIFIEDConfirmedCOC: GALLONS * OTHER INORGANIC SOLID WASTE Laboratory Waste Chemicals * EMPTY CONTAINERS, LESS THAN30PotentialCOC: NONESPECIFIEDPastUse: NONESPECIFIEDAPN: 117.0213Longitude: 32.59416Latitude: NotreportedFunding: NONESPECIFIEDSiteMgmtReq: NORestrictedUse: NotreportedSpecialProgram: 40Senate: 79Assembly: CleanupCypressDivisionBranch: Referred - NotAssignedSupervisor: NotreportedProgramManager: RWQCB 9 - SanDiegoLeadAgency: RWQCB 9 - SanDiegoRegulatoryAgencies: NONPL: NotreportedAcres: HistoricalSiteTypeDetailed: HistoricalSiteType: 400004SiteCode: 08/27/1990StatusDate: Refer: RWQCBStatus: 37500032FacilityID: ENVIROSTOR: 4038 ft. 0.765 mi. Relative: Lower Actual: 120 ft. 1/2-1 CHULA VISTA, CA 92011 WSW CA BOND EXP. PLAN4551OTAYVALLEYROAD N/A 27 CAENVIROSTORAPACHESERVICES S100833516 TC5146125.2s Page 99 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation San Diego RWQCB. responsible parties are continuing remediation work under the oversight of the site characterization is necessary to confirm the adequacy of cleanup. The chatacterization to determine the current levels of contamination. Additional Some subsequent surface removal occurred. There has been inadequate responsible party, when the salvage yard was destroyed by fire in August, 1985. Diego Region. DHS was working in coordination with the U.S. Navy, a potentially In February, 1981, a cleanup and abatement order was issued by the RWQCB, SanSiteActivityStatus: evaluated in the future to determine if additional cleanup action is necessary. through removal of the most highly contaminated soil. This site will be further water is within 12 feet of the surface. The site has been partially abated site. PCE and TCA were found in standing surface water and ground water. Ground There is some potential threat to the Otay River. Farmland is adjacent totheThreatToPublicHealth & Env: perchloroethylene (PCE). The site is located on fill material. solvents, electrical insulating oils, trichloroethane (TCA), chloroform, and Hazardous wastes previously stored and spilled include petroleum distillates, Soil contamination includes low levels of copper, zinc, cadmium and lead.Hazardous Waste Desc: associated with nearby naval facilities. The site was formerly a junkyard. Many of the wastes onsite are thought tobeSiteDescription: fund site cleanup, another source of funds will need to be identified. reimbursement to DHS for its oversight activities. If the RPs are unable to This site is projected to be remediated by the responsible partieswillProjectRevenueSourceDesc: NotreportedProjectRevenueSourceCity,St,Zip: NotreportedProjectRevenueSourceAddr: NotreportedProjectRevenueSourceCompany: BACKLOG SITE CLEANUP PLANNINGREPORTReponsibleParty: CA BOND EXP. PLAN: NotreportedScheduleRevisedDate: NotreportedScheduleDueDate: NotreportedScheduleDocumentType: NotreportedScheduleSubAreaName: NotreportedScheduleAreaName: NotreportedFutureDueDate: NotreportedFutureDocumentType: NotreportedFutureSubAreaName: NotreportedFutureAreaName: IMPLIMENTING PLAN INSURING NO TOXINS WILL BE RELEASED PROBABILITY TOXINS WILL BE RELEASED. RWQCB IS LEAD AGENCY AND IS PRELIM ASSESS DONE STUDY DONE FOR RWQCB STATES THERE ISLOWComments: 02/19/1987CompletedDate: APACHE SERVICES (Continued)S100833516 NotreportedAcres: HistoricalSiteTypeDetailed: HistoricalSiteType: 400112SiteCode: 04/25/1995StatusDate: Refer: RWQCBStatus: 37490031FacilityID: ENVIROSTOR: 4773 ft. Site 1 of 4 in cluster I 0.904 mi. Relative: Higher Actual: 349 ft. 1/2-1 CHULA VISTA, CA 92011 ENE OTAY VALLEY ROAD N/A I28 CAENVIROSTOROTAYSANITARYLANDFILL S101481986 TC5146125.2s Page 100 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedScheduleRevisedDate: NotreportedScheduleDueDate: NotreportedScheduleDocumentType: NotreportedScheduleSubAreaName: NotreportedScheduleAreaName: NotreportedFutureDueDate: NotreportedFutureDocumentType: NotreportedFutureSubAreaName: NotreportedFutureAreaName: NotreportedComments: 11/04/2014CompletedDate: CorrespondenceCompletedDocumentType: NotreportedCompletedSubAreaName: PROJECTWIDECompletedAreaName: Completed Info: Envirostor IDNumberAliasType: 37490031AliasName: Project Code (Site Code)Alias Type: 400112AliasName: PCodeAliasType: P43072AliasName: NONESPECIFIEDPotentialDescription: NONESPECIFIEDConfirmedCOC: NONESPECIFIEDPotentialCOC: NONESPECIFIEDPastUse: NONESPECIFIEDAPN: 0Longitude: 0Latitude: NotreportedFunding: NONESPECIFIEDSiteMgmtReq: NORestrictedUse: NotreportedSpecialProgram: NotreportedSenate: NotreportedAssembly: CleanupCypressDivisionBranch: Referred - NotAssignedSupervisor: NotreportedProgramManager: NONESPECIFIEDLeadAgency: NONESPECIFIEDRegulatoryAgencies: NONPL: OTAY SANITARY LANDFILL (Continued) S101481986 CDIPROCESSINGFacilityType2: MEDIUM VOLUME TRANSFER/ MEDIUM VOLUME CDIPROCESSINGFacilityType: OTAY LANDFILL, INCOperator: OTAY LANDFILL, INCOwnerName: 37-AA-0973SWISNumber: SANDIEGORegion: ACTIVEOperationalStatus: ACTIVESITESFacilityStatus: SAN DIEGO CO. LF: 4792 ft.CAHWPSite2of4inclusterI 0.908 mi.CA EMI Relative: Higher Actual: 349 ft. 1/2-1 CA HISTUSTCHULAVISTA, CA 92011 ENE CA San Diego Co. HMMD1700MAXWELLROAD N/A I29 CA SWF/LFALLIEDWASTE - OTAY LANDFILL U001571080 TC5146125.2s Page 101 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 210800PermitNumber: NotreportedHazardousCategories2: ACUTEHazardousCategories1: MaterialMaterialWaste: ANTIFREEZEOtherInformation: ETHYLENEGLYCOLName: 107-21-1CaseNumber: 11/02/2012UpdateDate: 210800PermitNumber: NotreportedHazardousCategories2: FIREHazardousCategories1: MaterialMaterialWaste: NotreportedOtherInformation: ACETYLENEGASName: 74-86-2CaseNumber: 11/02/2012UpdateDate: 210800PermitNumber: Inventory Active Permits (not SQG Medical): NotreportedGenerateMedicalWaste: NotreportedTreatHazWaste: NotreportedGenerateHazWaste: NotreportedSubjectToAPSA: NotreportedOwnOrOperateUST: NotreportedHandleRegulatedHazmat: NotreportedUSTOwner: 90703FacilityMailingZip: CAFacilityMailingState: CERRITOSFacilityMailingCity: 14150 VINEPLACEFacilityMailingAddress: ECOLOGY AUTO PARTS, INCFacilityOwner: 11/02/2012DateLastUpdated: 09/30/2013PermitExpiration: OPENPermitStatus: 619-429-3497FacilityTelephone: 01/26/2011LastHMMDInspection: 644-230-19-00APN: CAL000341724EPAIdNumber: 6HK26BusinessType: 210800PermitNumber: HMMD SAN DIEGO: QUARTERLYInspectionFrequency: EANOTIFICATIONPERMTIER: GREEN MATERIAL COMPOSTING OPERATION (>12,500yd3)Facility Type2: ORGANIC MATERIALS HANDLINGFACILITIESFacilityType: PLANTS CHOICE, INCOperator: BEND HOEOOIOwnerName: 37-AA-0975SWISNumber: SANDIEGORegion: ACTIVEOperationalStatus: ACTIVESITESFacilityStatus: MONTHLYInspectionFrequency: REGISTRATIONPERMTIER: ALLIED WASTE - OTAY LANDFILL (Continued)U001571080 TC5146125.2s Page 102 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation WASTE 888 USED OILFILTERSName: NotreportedCaseNumber: 11/02/2012UpdateDate: 210800PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: 1X55GAL USED/1X55 GAL NEW/ XOGUARDFLUIDOtherInformation: WASTE 342 ORGANIC LIQUIDS W/METALSName: NotreportedCaseNumber: 11/02/2012UpdateDate: 210800PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: OILYABSORBENTOtherInformation: WASTE 223 UNSPEC OIL CONTAININGWASTEName: NotreportedCaseNumber: 11/02/2012UpdateDate: 210800PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: USEDOILOtherInformation: WASTE 221 WASTE OIL & MIXEDOILName: NotreportedCaseNumber: 11/02/2012UpdateDate: 210800PermitNumber: NotreportedHazardousCategories2: PRESSURERELEASEHazardousCategories1: MaterialMaterialWaste: NotreportedOtherInformation: PROPANEName: 68476-85-7CaseNumber: 11/02/2012UpdateDate: 210800PermitNumber: NotreportedHazardousCategories2: PRESSURERELEASEHazardousCategories1: MaterialMaterialWaste: NotreportedOtherInformation: OXYGENGASName: 7782-44-7CaseNumber: 11/02/2012UpdateDate: 210800PermitNumber: NotreportedHazardousCategories2: CHRONICHazardousCategories1: MaterialMaterialWaste: NotreportedOtherInformation: OILS, LUBRICATINGName: 8002-05-9CaseNumber: 11/02/2012UpdateDate: ALLIED WASTE - OTAY LANDFILL (Continued)U001571080 TC5146125.2s Page 103 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation MotorOilCommonName: NotreportedChemicalName: 2016-08-31T02:32:30.000LastUpdated: PureHazardousMaterialType: NTradeSecret: DEH2016-HCHEM-0107271ChildRecordId: YActivePermit: PermitRenewedPermitStatus: DEH2009-HUPFP-210800RecordID: Waste and Materials: NotreportedGenerateMedicalWaste: NTreatHazWaste: YGenerateHazWaste: NotreportedSubjectToAPSA: NotreportedOwnOrOperateUST: NotreportedHandleRegulatedHazmat: NUSTOwner: NotreportedFacilityMailingZip: NotreportedFacilityMailingState: NotreportedFacilityMailingCity: 14150 VINE PLACE, CERRITOS, CA90703FacilityMailingAddress: NotreportedFacilityOwner: 04/05/2017DateLastUpdated: NotreportedPermitExpiration: PermitRenewedPermitStatus: 562-921-9974FacilityTelephone: NotreportedLastHMMDInspection: NotreportedAPN: CAL000341724EPAIdNumber: NotreportedBusinessType: NotreportedPermitNumber: ACTIVEActivity: generation of hazardous waste. 68.905 A Unified Program Facility permit has not been obtained fortheViolationCitation: UPF Permit NOT OBTAINED forHAZWASTEViolation: 6HV0131ViolationCode: 05/28/2009InspectionDate: 11/02/2012UpdateDate: 210800PermitNumber: ACTIVEActivity: materials. 68.905 A Unified Program Facility permit has not been obtained forhazardousViolationCitation: NO UPF PERMIT FORHAZMATSViolation: 6HV1001ViolationCode: 05/28/2009InspectionDate: 11/02/2012UpdateDate: 210800PermitNumber: Violations Active Permits: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: DRAINED - TOECOLOGYOtherInformation: ALLIED WASTE - OTAY LANDFILL (Continued) U001571080 TC5146125.2s Page 104 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedCaseNumber: Diesel Exhaust Fluid (DEF)Common Name: NotreportedChemicalName: 2016-08-31T02:32:30.000LastUpdated: PureHazardousMaterialType: NTradeSecret: DEH2016-HCHEM-0107269ChildRecordId: YActivePermit: PermitRenewedPermitStatus: DEH2009-HUPFP-210800RecordID: NotreportedCaseNumber: HYDRAULICOILCommonName: HYDRAULICOILChemicalName: 2016-08-31T02:32:30.000LastUpdated: PureHazardousMaterialType: NTradeSecret: DEH2016-HCHEM-0107268ChildRecordId: YActivePermit: PermitRenewedPermitStatus: DEH2009-HUPFP-210800RecordID: NotreportedCaseNumber: GearOilCommonName: GearOilChemicalName: 2016-08-31T02:32:30.000LastUpdated: PureHazardousMaterialType: NTradeSecret: DEH2016-HCHEM-0107267ChildRecordId: YActivePermit: PermitRenewedPermitStatus: DEH2009-HUPFP-210800RecordID: 107-21-1CaseNumber: ANTIFREEZECommonName: EthyleneGlycolChemicalName: 2016-08-31T02:32:30.000LastUpdated: PureHazardousMaterialType: NTradeSecret: DEH2016-HCHEM-0107266ChildRecordId: YActivePermit: PermitRenewedPermitStatus: DEH2009-HUPFP-210800RecordID: 7782-44-7CaseNumber: OXYGENGASCommonName: OXYGENGASChemicalName: 2016-08-31T02:32:30.000LastUpdated: PureHazardousMaterialType: NTradeSecret: DEH2016-HCHEM-0107265ChildRecordId: YActivePermit: PermitRenewedPermitStatus: DEH2009-HUPFP-210800RecordID: NotreportedCaseNumber: ALLIED WASTE - OTAY LANDFILL (Continued)U001571080 TC5146125.2s Page 105 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 210800PermitNumber: NotreportedCaseNumber: Oily Water (Parts Washer)Common Name: NotreportedChemicalName: 2016-08-31T02:32:30.000LastUpdated: NotreportedHazardousMaterialType: NTradeSecret: DEH2016-HWAST-0088523ChildRecordId: YActivePermit: PermitRenewedPermitStatus: DEH2009-HUPFP-210800RecordID: NotreportedCaseNumber: Ethylene Glycol (Waste)Common Name: EthyleneGlycolChemicalName: 2016-08-31T02:32:30.000LastUpdated: NotreportedHazardousMaterialType: NTradeSecret: DEH2016-HWAST-0088522ChildRecordId: YActivePermit: PermitRenewedPermitStatus: DEH2009-HUPFP-210800RecordID: NotreportedCaseNumber: USEDOILCommonName: WASTE 221 WASTE OIL & MIXEDOILChemicalName: 2016-08-31T02:32:30.000LastUpdated: NotreportedHazardousMaterialType: NTradeSecret: DEH2016-HWAST-0088521ChildRecordId: YActivePermit: PermitRenewedPermitStatus: DEH2009-HUPFP-210800RecordID: NotreportedCaseNumber: OILY SOIL/SOLIDSCommonName: WASTE 611 CONTAMINATEDSOILChemicalName: 2016-08-31T02:32:30.000LastUpdated: NotreportedHazardousMaterialType: NTradeSecret: DEH2016-HWAST-0088520ChildRecordId: YActivePermit: PermitRenewedPermitStatus: DEH2009-HUPFP-210800RecordID: 74-98-6CaseNumber: Liquefied Petroleum Gas (lpg)Common Name: PropaneChemicalName: 2016-08-31T02:32:30.000LastUpdated: PureHazardousMaterialType: NTradeSecret: DEH2016-HCHEM-0107270ChildRecordId: YActivePermit: PermitRenewedPermitStatus: DEH2009-HUPFP-210800RecordID: ALLIED WASTE - OTAY LANDFILL (Continued)U001571080 TC5146125.2s Page 106 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedHazardousCategories2: PRESSURERELEASEHazardousCategories1: MaterialMaterialWaste: NotreportedOtherInformation: OXYGENGASName: 7782-44-7CaseNumber: 11/02/2012UpdateDate: 210800PermitNumber: NotreportedHazardousCategories2: CHRONICHazardousCategories1: MaterialMaterialWaste: NotreportedOtherInformation: OILS, LUBRICATINGName: 8002-05-9CaseNumber: 11/02/2012UpdateDate: 210800PermitNumber: NotreportedHazardousCategories2: ACUTEHazardousCategories1: MaterialMaterialWaste: ANTIFREEZEOtherInformation: ETHYLENEGLYCOLName: 107-21-1CaseNumber: 11/02/2012UpdateDate: 210800PermitNumber: NotreportedHazardousCategories2: FIREHazardousCategories1: MaterialMaterialWaste: NotreportedOtherInformation: ACETYLENEGASName: 74-86-2CaseNumber: 11/02/2012UpdateDate: 210800PermitNumber: Inventory Active Permits (not SQG Medical): NotreportedGenerateMedicalWaste: NotreportedTreatHazWaste: YGenerateHazWaste: NotreportedSubjectToAPSA: NotreportedOwnOrOperateUST: YHandleRegulatedHazmat: NotreportedUSTOwner: 90703FacilityMailingZip: CAFacilityMailingState: CERRITOSFacilityMailingCity: 14150 VINEPLACEFacilityMailingAddress: ECOLOGY AUTO PARTS, INCFacilityOwner: 11/02/2012DateLastUpdated: 09/30/2013PermitExpiration: OPENPermitStatus: 619-429-3497FacilityTelephone: 01/26/2011LastHMMDInspection: 644-230-19-00APN: CAL000341724EPAIdNumber: 6HK26BusinessType: ALLIED WASTE - OTAY LANDFILL (Continued)U001571080 TC5146125.2s Page 107 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 11/02/2012UpdateDate: 210800PermitNumber: ACTIVEActivity: materials. 68.905 A Unified Program Facility permit has not been obtained forhazardousViolationCitation: NO UPF PERMIT FORHAZMATSViolation: 6HV1001ViolationCode: 05/28/2009InspectionDate: 11/02/2012UpdateDate: 210800PermitNumber: Violations Active Permits: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: DRAINED - TOECOLOGYOtherInformation: WASTE 888 USED OILFILTERSName: NotreportedCaseNumber: 11/02/2012UpdateDate: 210800PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: 1X55GAL USED/1X55 GAL NEW/ XOGUARDFLUIDOtherInformation: WASTE 342 ORGANIC LIQUIDS W/METALSName: NotreportedCaseNumber: 11/02/2012UpdateDate: 210800PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: OILYABSORBENTOtherInformation: WASTE 223 UNSPEC OIL CONTAININGWASTEName: NotreportedCaseNumber: 11/02/2012UpdateDate: 210800PermitNumber: NotreportedHazardousCategories2: NotreportedHazardousCategories1: WasteMaterialWaste: USEDOILOtherInformation: WASTE 221 WASTE OIL & MIXEDOILName: NotreportedCaseNumber: 11/02/2012UpdateDate: 210800PermitNumber: NotreportedHazardousCategories2: PRESSURERELEASEHazardousCategories1: MaterialMaterialWaste: NotreportedOtherInformation: PROPANEName: 68476-85-7CaseNumber: 11/02/2012UpdateDate: 210800PermitNumber: ALLIED WASTE - OTAY LANDFILL (Continued) U001571080 TC5146125.2s Page 108 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 4953SICCode: SDAirDistrictName: 7263FacilityID: SDAirBasin: 37CountyCode: 1996Year: EMI: VisualLeakDetection: 6ContainerConstructionThickness: NotreportedTypeofFuel: WASTETankUsedfor: 00013500TankCapacity: 1982YearInstalled: SOGContainerNum: 003TankNum: Visual, Groundwater MonitoringWellLeakDetection: 6ContainerConstructionThickness: NotreportedTypeofFuel: WASTETankUsedfor: 00250000TankCapacity: 1982YearInstalled: SF2ContainerNum: 002TankNum: Visual, Groundwater MonitoringWellLeakDetection: 6ContainerConstructionThickness: NotreportedTypeofFuel: WASTETankUsedfor: 00250000TankCapacity: 1982YearInstalled: SF1ContainerNum: 001TankNum: 0003TotalTanks: TORRANCE, CA90505OwnerCity,St,Zip: 2550 237THSTREETOwnerAddress: BKKCORPORATIONOwnerName: 6194211175Telephone: HERBSMITHContactName: TREATMENTFACILITYOtherType: OtherFacilityType: 00000016754FacilityID: STATERegion: NotreportedURL: NotreportedFileNumber: HIST UST: ACTIVEActivity: generation of hazardous waste. 68.905 A Unified Program Facility permit has not been obtained fortheViolationCitation: UPF Permit NOT OBTAINED forHAZWASTEViolation: 6HV0131ViolationCode: 05/28/2009InspectionDate: ALLIED WASTE - OTAY LANDFILL (Continued) U001571080 TC5146125.2s Page 109 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 1CarbonMonoxideEmissionsTons/Yr: 12ReactiveOrganicGasesTons/Yr: 1485TotalOrganicHydrocarbonGasesTons/Yr: NotreportedConsolidatedEmissionReportingRule: NotreportedCommunityHealthAirPollutionInfoSystem: SAN DIEGO COUNTYAPCDAirDistrictName: 4953SICCode: SDAirDistrictName: 7263FacilityID: SDAirBasin: 37CountyCode: 1999Year: 22Part. Matter 10 Micrometers and Smllr Tons/Yr: 84ParticulateMatterTons/Yr: 0SOX - Oxides of Sulphur Tons/Yr: 0NOX - Oxides of Nitrogen Tons/Yr: 1CarbonMonoxideEmissionsTons/Yr: 12ReactiveOrganicGasesTons/Yr: 1485TotalOrganicHydrocarbonGasesTons/Yr: NotreportedConsolidatedEmissionReportingRule: NotreportedCommunityHealthAirPollutionInfoSystem: SAN DIEGO COUNTYAPCDAirDistrictName: 4953SICCode: SDAirDistrictName: 7263FacilityID: SDAirBasin: 37CountyCode: 1998Year: 17Part. Matter 10 Micrometers and Smllr Tons/Yr: 58ParticulateMatterTons/Yr: 0SOX - Oxides of Sulphur Tons/Yr: 2NOX - Oxides of Nitrogen Tons/Yr: 1CarbonMonoxideEmissionsTons/Yr: 13ReactiveOrganicGasesTons/Yr: 1623TotalOrganicHydrocarbonGasesTons/Yr: NotreportedConsolidatedEmissionReportingRule: NotreportedCommunityHealthAirPollutionInfoSystem: SAN DIEGO COUNTYAPCDAirDistrictName: 4953SICCode: SDAirDistrictName: 7263FacilityID: SDAirBasin: 37CountyCode: 1997Year: 37Part. Matter 10 Micrometers and Smllr Tons/Yr: 84ParticulateMatterTons/Yr: 0SOX - Oxides of Sulphur Tons/Yr: 3NOX - Oxides of Nitrogen Tons/Yr: 7CarbonMonoxideEmissionsTons/Yr: 70ReactiveOrganicGasesTons/Yr: 5786TotalOrganicHydrocarbonGasesTons/Yr: NotreportedConsolidatedEmissionReportingRule: NotreportedCommunityHealthAirPollutionInfoSystem: SAN DIEGO COUNTYAPCDAirDistrictName: ALLIED WASTE - OTAY LANDFILL (Continued)U001571080 TC5146125.2s Page 110 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 2003Year: 87Part. Matter 10 Micrometers and Smllr Tons/Yr: 228ParticulateMatterTons/Yr: 2SOX - Oxides of Sulphur Tons/Yr: 8NOX - Oxides of Nitrogen Tons/Yr: 2CarbonMonoxideEmissionsTons/Yr: 17ReactiveOrganicGasesTons/Yr: 2045TotalOrganicHydrocarbonGasesTons/Yr: NotreportedConsolidatedEmissionReportingRule: YCommunityHealthAirPollutionInfoSystem: SAN DIEGO COUNTYAPCDAirDistrictName: 4953SICCode: SDAirDistrictName: 7263FacilityID: SDAirBasin: 37CountyCode: 2002Year: 66Part. Matter 10 Micrometers and Smllr Tons/Yr: 239ParticulateMatterTons/Yr: 0SOX - Oxides of Sulphur Tons/Yr: 0NOX - Oxides of Nitrogen Tons/Yr: 2CarbonMonoxideEmissionsTons/Yr: 30ReactiveOrganicGasesTons/Yr: 3695TotalOrganicHydrocarbonGasesTons/Yr: NotreportedConsolidatedEmissionReportingRule: YCommunityHealthAirPollutionInfoSystem: SAN DIEGO COUNTYAPCDAirDistrictName: 4953SICCode: SDAirDistrictName: 7263FacilityID: SDAirBasin: 37CountyCode: 2001Year: 66Part. Matter 10 Micrometers and Smllr Tons/Yr: 239ParticulateMatterTons/Yr: 0SOX - Oxides of Sulphur Tons/Yr: 0NOX - Oxides of Nitrogen Tons/Yr: 2CarbonMonoxideEmissionsTons/Yr: 30ReactiveOrganicGasesTons/Yr: 3695TotalOrganicHydrocarbonGasesTons/Yr: NotreportedConsolidatedEmissionReportingRule: NotreportedCommunityHealthAirPollutionInfoSystem: SAN DIEGO COUNTYAPCDAirDistrictName: 4953SICCode: SDAirDistrictName: 7263FacilityID: SDAirBasin: 37CountyCode: 2000Year: 22Part. Matter 10 Micrometers and Smllr Tons/Yr: 84ParticulateMatterTons/Yr: 0SOX - Oxides of Sulphur Tons/Yr: 0NOX - Oxides of Nitrogen Tons/Yr: ALLIED WASTE - OTAY LANDFILL (Continued)U001571080 TC5146125.2s Page 111 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation Historical - Non-OperatingFacilityType: CAT080010101EPAId: 01/11/1983ActualDate: New Operating Permit - FINAL PERMIT (EFFECTIVE)Event Description: CONTAIN1 (GPRA Unit), TANKSTR1 (GPRA Unit), TANKTRT1 (GPRA Unit)Unit Names: Historical - Non-OperatingFacilityType: CAT080010101EPAId: Activities: NotreportedPublicInformationOfficer: NotreportedPublicInformationOfficer: 40SenateDistrict: 79AssemblyDistrict: NotreportedSiteCode: NotreportedSupervisor: NotreportedTeam: NotreportedFacilitySize: Historical - Non-OperatingFacilityType: 117.0182Longitude: 32.59757Latitude: CLOSEDCleanupStatus: CAT080010101EPAId: HWP: 86.8528861Part. Matter 10 Micrometers and Smllr Tons/Yr: 228.336762ParticulateMatterTons/Yr: 1.547272SOX - Oxides of Sulphur Tons/Yr: 8.432NOX - Oxides of Nitrogen Tons/Yr: 1.5757CarbonMonoxideEmissionsTons/Yr: 16.9134257ReactiveOrganicGasesTons/Yr: 2044.525658TotalOrganicHydrocarbonGasesTons/Yr: NotreportedConsolidatedEmissionReportingRule: YCommunityHealthAirPollutionInfoSystem: SAN DIEGO COUNTYAPCDAirDistrictName: 4953SICCode: SDAirDistrictName: 7263FacilityID: SDAirBasin: 37CountyCode: 2004Year: 87Part. Matter 10 Micrometers and Smllr Tons/Yr: 228ParticulateMatterTons/Yr: 2SOX - Oxides of Sulphur Tons/Yr: 8NOX - Oxides of Nitrogen Tons/Yr: 2CarbonMonoxideEmissionsTons/Yr: 17ReactiveOrganicGasesTons/Yr: 2045TotalOrganicHydrocarbonGasesTons/Yr: NotreportedConsolidatedEmissionReportingRule: NotreportedCommunityHealthAirPollutionInfoSystem: SAN DIEGO COUNTYAPCDAirDistrictName: 4953SICCode: SDAirDistrictName: 7263FacilityID: SDAirBasin: 37CountyCode: ALLIED WASTE - OTAY LANDFILL (Continued)U001571080 TC5146125.2s Page 112 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 08/19/1982ActualDate: New Operating Permit - TECHNICAL COMPLETELETTEREventDescription: CONTAIN1 (GPRA Unit), TANKSTR1 (GPRA Unit), TANKTRT1 (GPRA Unit)Unit Names: Historical - Non-OperatingFacilityType: CAT080010101EPAId: 06/30/1993ActualDate: Renewal - Historical - FINAL PERMIT RENEWAL (EFFECTIVE)Event Description: CONTAIN1 (GPRA Unit), TANKSTR1 (GPRA Unit), TANKTRT1 (GPRA Unit)Unit Names: Historical - Non-OperatingFacilityType: CAT080010101EPAId: 05/31/1989ActualDate: Renewal - Historical - APPLICATION PART BRECEIVEDEventDescription: CONTAIN1 (GPRA Unit), TANKSTR1 (GPRA Unit), TANKTRT1 (GPRA Unit)Unit Names: Historical - Non-OperatingFacilityType: CAT080010101EPAId: 05/17/1990ActualDate: New Operating Permit - APPLICATION PART ARECEIVEDEventDescription: CONTAIN1 (GPRA Unit), TANKSTR1 (GPRA Unit), TANKTRT1 (GPRA Unit)Unit Names: Historical - Non-OperatingFacilityType: CAT080010101EPAId: 01/11/1988ActualDate: New Operating Permit - FINAL PERMIT (EXPIRES)Event Description: CONTAIN1 (GPRA Unit), TANKSTR1 (GPRA Unit), TANKTRT1 (GPRA Unit)Unit Names: Historical - Non-OperatingFacilityType: CAT080010101EPAId: 01/11/1983ActualDate: New Operating Permit - FINALPERMITEventDescription: CONTAIN1 (GPRA Unit), TANKSTR1 (GPRA Unit), TANKTRT1 (GPRA Unit)Unit Names: Historical - Non-OperatingFacilityType: CAT080010101EPAId: 03/31/1992ActualDate: Renewal - Historical - FINAL PERMITRENEWALEventDescription: CONTAIN1 (GPRA Unit), TANKSTR1 (GPRA Unit), TANKTRT1 (GPRA Unit)Unit Names: Historical - Non-OperatingFacilityType: CAT080010101EPAId: 08/06/1982ActualDate: New Operating Permit - PUBLIC COMMENT (BEGIN)Event Description: CONTAIN1 (GPRA Unit), TANKSTR1 (GPRA Unit), TANKTRT1 (GPRA Unit)Unit Names: Historical - Non-OperatingFacilityType: CAT080010101EPAId: 04/26/1982ActualDate: New Operating Permit - APPLICATION PART BRECEIVEDEventDescription: CONTAIN1 (GPRA Unit), TANKSTR1 (GPRA Unit), TANKTRT1 (GPRA Unit)Unit Names: Historical - Non-OperatingFacilityType: CAT080010101EPAId: 06/25/1991ActualDate: Renewal - Historical - TECHNICAL COMPLETELETTEREventDescription: CONTAIN1 (GPRA Unit), TANKSTR1 (GPRA Unit), TANKTRT1 (GPRA Unit)Unit Names: ALLIED WASTE - OTAY LANDFILL (Continued) U001571080 TC5146125.2s Page 113 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 37730291Alias: Envirostor IDNumberAliasType: Historical - Non-OperatingFacilityType: CAT080010101EPAId: 110000832243Alias: FRSAliasType: Historical - Non-OperatingFacilityType: CAT080010101EPAId: Alias: 11/25/1998ActualDate: Closure Final - ISSUE CLOSUREVERIFICATIONEventDescription: CONTAIN1 (GPRA Unit), TANKSTR1 (GPRA Unit), TANKTRT1 (GPRA Unit)Unit Names: Historical - Non-OperatingFacilityType: CAT080010101EPAId: 06/17/1998ActualDate: Closure Final - RECEIVE CLOSURECERTIFICATIONEventDescription: CONTAIN1 (GPRA Unit), TANKSTR1 (GPRA Unit), TANKTRT1 (GPRA Unit)Unit Names: Historical - Non-OperatingFacilityType: CAT080010101EPAId: Closure: 06/29/1991ActualDate: Renewal - Historical - PUBLIC COMMENT (BEGIN)Event Description: CONTAIN1 (GPRA Unit), TANKSTR1 (GPRA Unit), TANKTRT1 (GPRA Unit)Unit Names: Historical - Non-OperatingFacilityType: CAT080010101EPAId: ALLIED WASTE - OTAY LANDFILL (Continued) U001571080 NONESPECIFIEDSiteMgmtReq: NORestrictedUse: NotreportedSpecialProgram: 40Senate: 79Assembly: CleanupCypressDivisionBranch: UnknownSupervisor: NotreportedProgramManager: WMLeadAgency: SMBRPRegulatoryAgencies: NONPL: 0Acres: CorrectiveActionSiteTypeDetailed: CorrectiveActionSiteType: NotreportedSiteCode: 01/01/2008StatusDate: InactiveStatus: 80001820FacilityID: ENVIROSTOR: CA NPDES 4792 ft.CA FinancialAssuranceSite3of4inclusterI 0.908 mi.CA ENF Relative: Higher Actual: 349 ft. 1/2-1 CALDSCHULAVISTA, CA 91911 ENE CA SWF/LF1700MAXWELLRD N/A I30 CAENVIROSTORAPPROPRIATETECHNOLOGIESIIINC S109287760 TC5146125.2s Page 114 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation Sites With No OperableUnitCompletedAreaName: NotreportedComments: 08/12/2010CompletedDate: Human ExposureControlledCompletedDocumentType: NotreportedCompletedSubAreaName: PROJECTWIDECompletedAreaName: the lead for this landfill. facility was constructed on a closed class I lsndfill which SD WB is necessary for Washout Pit and Unlined Effluent Pippes. However, this The RFI report indicated there is no further investigationisComments: 02/22/1995CompletedDate: RFIReportCompletedDocumentType: WASHOUT PIT & OLD UNLINED EFFLUENTPIPESCompletedSubAreaName: Sites With No OperableUnitCompletedAreaName: NotreportedComments: 09/15/1989CompletedDate: Preliminary AssessmentReportCompletedDocumentType: NotreportedCompletedSubAreaName: PROJECTWIDECompletedAreaName: NotreportedComments: 06/14/1994CompletedDate: RFIWorkplanCompletedDocumentType: WASHOUT PIT & OLD UNLINED EFFLUENTPIPESCompletedSubAreaName: Sites With No OperableUnitCompletedAreaName: NotreportedComments: 11/01/1987CompletedDate: Preliminary AssessmentReportCompletedDocumentType: NotreportedCompletedSubAreaName: PROJECTWIDECompletedAreaName: NotreportedComments: 12/08/2010CompletedDate: Groundwater MigrationControlledCompletedDocumentType: NotreportedCompletedSubAreaName: PROJECTWIDECompletedAreaName: Completed Info: Envirostor IDNumberAliasType: 80001820AliasName: Envirostor IDNumberAliasType: 37730291AliasName: EPA (FRS #)Alias Type: 110000832243AliasName: EPA IdentificationNumberAliasType: CAT080010101AliasName: NONESPECIFIEDPotentialDescription: NONESPECIFIEDConfirmedCOC: NONESPECIFIEDPotentialCOC: NONESPECIFIEDPastUse: NONESPECIFIEDAPN: 117.0182Longitude: 32.59757Latitude: NotreportedFunding: APPROPRIATE TECHNOLOGIES II INC (Continued) S109287760 TC5146125.2s Page 115 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedScheduleRevisedDate: NotreportedScheduleDueDate: NotreportedScheduleDocumentType: NotreportedScheduleSubAreaName: NotreportedScheduleAreaName: NotreportedFutureDueDate: NotreportedFutureDocumentType: NotreportedFutureSubAreaName: NotreportedFutureAreaName: NotreportedComments: 12/08/2010CompletedDate: RemedyConstructedCompletedDocumentType: NotreportedCompletedSubAreaName: PROJECTWIDECompletedAreaName: NotreportedComments: 09/20/2011CompletedDate: Human ExposureControlledCompletedDocumentType: NotreportedCompletedSubAreaName: PROJECTWIDECompletedAreaName: NotreportedComments: 06/29/1993CompletedDate: Historical Operating PermitAuthorityCompletedDocumentType: NotreportedCompletedSubAreaName: PROJECTWIDECompletedAreaName: NotreportedComments: 09/20/2011CompletedDate: Groundwater MigrationControlledCompletedDocumentType: NotreportedCompletedSubAreaName: PROJECTWIDECompletedAreaName: NotreportedComments: 09/20/2011CompletedDate: RemedyConstructedCompletedDocumentType: NotreportedCompletedSubAreaName: PROJECTWIDECompletedAreaName: NotreportedComments: 06/29/1991CompletedDate: RCRA Facility AssessmentReportCompletedDocumentType: WASHOUT PIT & OLD UNLINED EFFLUENTPIPESCompletedSubAreaName: Sites With No OperableUnitCompletedAreaName: NotreportedComments: 09/28/1992CompletedDate: Interim MeasuresQuestionnaireCompletedDocumentType: WASHOUT PIT & OLD UNLINED EFFLUENTPIPESCompletedSubAreaName: Sites With No OperableUnitCompletedAreaName: NotreportedComments: 05/27/1989CompletedDate: RCRA Facility AssessmentReportCompletedDocumentType: WASHOUT PIT & OLD UNLINED EFFLUENTPIPESCompletedSubAreaName: APPROPRIATE TECHNOLOGIES II INC (Continued) S109287760 TC5146125.2s Page 116 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation WASTES-PCB’S,EXPLOSIVE, & RADIOACTIVE MATLS. BKK/AP-TECII OPER PLAN - WST IN DRUMS OR OTHER APPROVED CONTAINERS UNACCEPTABLE ACCEPTS HAZ/NON-HAZ LIQ SLUDGE & SLURRY WASTES IN BULK, HAZ LIQ/SOLID PERMIT(OTHER) PERMIT: HAZ WASTE FAC PERMIT # CAT- 080010101 WASTE:Comments: 03/12/1984CompletedDate: Preliminary AssessmentReportCompletedDocumentType: NotreportedCompletedSubAreaName: PROJECTWIDECompletedAreaName: CALSITES VALIDATION PROGRAM CONFIRMS NFA FOR DTSC.Comments: 10/25/1994CompletedDate: SiteScreeningCompletedDocumentType: NotreportedCompletedSubAreaName: PROJECTWIDECompletedAreaName: Database Validation Program determines NFA for DTSC.Comments: 05/01/1995CompletedDate: SiteScreeningCompletedDocumentType: NotreportedCompletedSubAreaName: PROJECTWIDECompletedAreaName: Completed Info: Envirostor IDNumberAliasType: 37730291AliasName: Project Code (Site Code)Alias Type: 400205AliasName: EPA (FRS #)Alias Type: 110000832243AliasName: EPA IdentificationNumberAliasType: CAT080010101AliasName: AlternateNameAliasType: BKKCORPAliasName: NONESPECIFIEDPotentialDescription: NONESPECIFIEDConfirmedCOC: UNSPECIFIED AQUEOUSSOLUTIONPotentialCOC: NONESPECIFIEDPastUse: NONESPECIFIEDAPN: 117.0049Longitude: 32.60513Latitude: NotreportedFunding: NONESPECIFIEDSiteMgmtReq: NORestrictedUse: RCRA 3012 - Past Haz Waste Disp InvenSiteSpecialProgram: 40Senate: 79Assembly: CleanupCypressDivisionBranch: MmonroySupervisor: NotreportedProgramManager: NONESPECIFIEDLeadAgency: NONESPECIFIEDRegulatoryAgencies: NONPL: NotreportedAcres: HistoricalSiteTypeDetailed: HistoricalSiteType: 400205SiteCode: 05/01/1995StatusDate: Refer: RCRAStatus: 37730291FacilityID: APPROPRIATE TECHNOLOGIES II INC (Continued)S109287760 TC5146125.2s Page 117 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedRemainingCapacity: NotreportedPermittedCapacitywithUnits: NotreportedActualThroughputwithUnits: NotreportedPermittedThroughputwithUnits: NotreportedProgramType: NotreportedWasteDischargeRequirementNum: 37-AA-0010SWISNum: NotreportedDisposalAcreage: NotreportedClosureType: NotreportedClosureDate: GreenMaterialsAcceptedWaste: QuarterlyInspectionFrequency: 03UnitNumber: CompostingCategory: MapGISSource: Industrial,AgriculturalLanduseName: PermittedRegulationStatus: Chipping and Grinding Activity Fac./ Op.Activity: NotreportedPermittedAcreage: PermittedPermitStatus: 06/26/2017PermitDate: Santee, CA92071OperatorCity,St,Zip: 8514 Mast Blvd.Operator Address2: NotreportedOperatorAddress: 6194494053OperatorPhone: Otay Landfill Inc.Operator: ActiveOperationalStatus: Phoenix, AZ82054OwnerCity,St,Zip: 18500 N. AlliedWayOwnerAddress2: NotreportedOwnerAddress: 9547692400OwnerTelephone: RepublicServicesOwnerName: 32.60333 / -117.005Lat/Long: 37-AA-0010FacilityID: STATERegion: SWF/LF (SWIS): NotreportedScheduleRevisedDate: NotreportedScheduleDueDate: NotreportedScheduleDocumentType: NotreportedScheduleSubAreaName: NotreportedScheduleAreaName: NotreportedFutureDueDate: NotreportedFutureDocumentType: NotreportedFutureSubAreaName: NotreportedFutureAreaName: FACILITY IDENTIFIED ID FROMERRISComments: 10/12/1983CompletedDate: DiscoveryCompletedDocumentType: NotreportedCompletedSubAreaName: PROJECTWIDECompletedAreaName: DONE RCRA 3012 NO DISP ONSITE. ALL STORAGE TEMPORARY. SUBMIT TO EPA PRELIM ASSESS TREATMT,STORAGE,TRANSFER FAC ZONED FOR OPEN SPACE & PARK DEVELOPMENT 1)SOURCE ACT: LAND USE: SITE SURROUNDED BY OTAY LDFL. HAZ WASTE APPROPRIATE TECHNOLOGIES II INC (Continued)S109287760 TC5146125.2s Page 118 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedOperatorAddress: 6194494053OperatorPhone: Otay Landfill Inc.Operator: ActiveOperationalStatus: Santee, CA92071OwnerCity,St,Zip: 8514 Mast Blvd.Owner Address2: NotreportedOwnerAddress: 6194494053OwnerTelephone: Otay Landfill Inc.Owner Name: 32.60135 / -117.0128Lat/Long: 37-AA-0973FacilityID: STATERegion: 32.60333 / -117.005Lat/Long: CubicYardsRemainingCapacitywithUnits: 21194008RemainingCapacity: 61154000PermittedCapacitywithUnits: Tons/dayActualThroughputwithUnits: 6700PermittedThroughputwithUnits: Waste Acceptance Assurance Responsibilities,Remaining Capacity Landfill,Treated Wood BOE Reporting Disposal Facility,Composite_Lined _LF_Cell(s),FinancialProgramType: IIIWasteDischargeRequirementNum: 37-AA-0010SWISNum: 230.00DisposalAcreage: EstimatedClosureType: 02/28/2030ClosureDate: designated,Sludge (BioSolids),Tires Animals,Green Materials,Industrial,Inert,Mixed municipal,Other Agricultural,Ash,Construction/demolition,Contaminated soil,DeadAcceptedWaste: MonthlyInspectionFrequency: 01UnitNumber: DisposalCategory: MapGISSource: Industrial,AgriculturalLanduseName: PermittedRegulationStatus: Solid WasteLandfillActivity: 409.00PermittedAcreage: PermittedPermitStatus: 06/26/2017PermitDate: Santee, CA92071OperatorCity,St,Zip: 8514 Mast Blvd.Operator Address2: NotreportedOperatorAddress: 6194494053OperatorPhone: Otay Landfill Inc.Operator: ActiveOperationalStatus: Phoenix, AZ82054OwnerCity,St,Zip: 18500 N. AlliedWayOwnerAddress2: NotreportedOwnerAddress: 9547692400OwnerTelephone: RepublicServicesOwnerName: 32.60333 / -117.005Lat/Long: 37-AA-0010FacilityID: STATERegion: 32.60333 / -117.005Lat/Long: NotreportedRemainingCapacitywithUnits: APPROPRIATE TECHNOLOGIES II INC (Continued)S109287760 TC5146125.2s Page 119 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedProgramType: NotreportedWasteDischargeRequirementNum: 37-AA-0975SWISNum: NotreportedDisposalAcreage: NotreportedClosureType: NotreportedClosureDate: Green Materials,WoodwasteAcceptedWaste: QuarterlyInspectionFrequency: 01UnitNumber: CompostingCategory: MapGISSource: CommercialLanduseName: NotificationRegulationStatus: Composting Operation (Green Waste)Activity: 4.00PermittedAcreage: NotificationPermitStatus: 01/25/2016PermitDate: San Ysidro, CA92154OperatorCity,St,Zip: PO Box436050OperatorAddress2: Beng HoeOoiOperatorAddress: 6195859909OperatorPhone: Plants Choice, Inc.Operator: ActiveOperationalStatus: Santee, CA92071OwnerCity,St,Zip: 8514 Mast Blvd.Owner Address2: NotreportedOwnerAddress: 6194494053OwnerTelephone: Otay Landfill Inc.Owner Name: 32.60333 / -117.005Lat/Long: 37-AA-0975FacilityID: STATERegion: 32.60135 / -117.0128Lat/Long: Tons/yearRemainingCapacitywithUnits: NotreportedRemainingCapacity: 54288PermittedCapacitywithUnits: Tons/dayActualThroughputwithUnits: 174PermittedThroughputwithUnits: NotreportedProgramType: NotreportedWasteDischargeRequirementNum: 37-AA-0973SWISNum: NotreportedDisposalAcreage: NotreportedClosureType: NotreportedClosureDate: Asphalt Shingles,Construction/demolition,Inert,WoodwasteAcceptedWaste: MonthlyInspectionFrequency: 01UnitNumber: Transfer/ProcessingCategory: MapGISSource: Residential,CommercialLanduseName: PermittedRegulationStatus: Medium Vol CDI Debris Proc. Fac.Activity: 5.50PermittedAcreage: PermittedPermitStatus: 07/09/2014PermitDate: Santee, CA92071OperatorCity,St,Zip: 8514 Mast Blvd.Operator Address2: APPROPRIATE TECHNOLOGIES II INC (Continued)S109287760 TC5146125.2s Page 120 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation County of San Diego Department ofEnvironmentalLocalEnforcementAgency: N/AEndingOperationDate: N/ABeginningOperationDate: 37-AA-0010SiteSWISNumber: Out-of-CountyFacilitySiteType: http://www.sandiego.gov/environmental-services/recycling/locations/otaylandfill.Site Website: NotreportedSiteEmail: 619) 421-5192SiteContactPhone: NotreportedSiteContact: N/AAlt. Address: 2718SiteID: LOS ANGELES CO. LF: 32.60436 / -117.00536Lat/Long: Tons/yearRemainingCapacitywithUnits: NotreportedRemainingCapacity: 11000PermittedCapacitywithUnits: Tons/weekActualThroughputwithUnits: 210PermittedThroughputwithUnits: NotreportedProgramType: NotreportedWasteDischargeRequirementNum: 37-AA-0984SWISNum: NotreportedDisposalAcreage: NotreportedClosureType: NotreportedClosureDate: FoodWastesAcceptedWaste: QuarterlyInspectionFrequency: 01UnitNumber: CompostingCategory: MapGISSource: ResidentialLanduseName: NotificationRegulationStatus: Composting Operation (Research)Activity: 4.00PermittedAcreage: NotificationPermitStatus: 12/18/2015PermitDate: Chula Vista, CA91912OperatorCity,St,Zip: 1700 Maxwell Rd.Operator Address2: NeilMohrOperatorAddress: 6194213773OperatorPhone: Otay Landfill, Inc.Operator: ActiveOperationalStatus: Chula Vista, CA91912OwnerCity,St,Zip: 1700 Maxwell Rd.Owner Address2: NeilMohrOwnerAddress: 6194213773OwnerTelephone: Otay Landfill, Inc.Owner Name: 32.60436 / -117.00536Lat/Long: 37-AA-0984FacilityID: STATERegion: 32.60333 / -117.005Lat/Long: Tons/yearRemainingCapacitywithUnits: NotreportedRemainingCapacity: 40000PermittedCapacitywithUnits: Tons/dayActualThroughputwithUnits: 200PermittedThroughputwithUnits: APPROPRIATE TECHNOLOGIES II INC (Continued)S109287760 TC5146125.2s Page 121 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation and Order 93-86 (General WDRS). Both sets of WDRs are available from issued by the San Diego Water Board as Order 90-009 (individual WDRs) Active Class III Landfill covered by waste dischargerequrementsSiteHistory: Oxygenates, Other Petroleum, Total Petroleum Hydrocarbons (TPH) Nitrate, Other inorganic / salt, Lead, MTBE / TBA / Other Fuel Other Solvent or Non-Petroleum Hydrocarbon, Trichloroethylene (TCE),Potential Contaminants of Concern: L10009614226EDRLinkID: NotreportedPotentialMediaAffect: RegionalBoardFileLocation: NotreportedLOCCaseNumber: 9000000214RBCaseNumber: NotreportedLocalAgency: JROCaseworker: SAN DIEGO RWQCB (REGION 9)Lead Agency: 07/20/2010StatusDate: Open - OperatingStatus: Land DisposalSiteCaseType: 117.0048Longitude: 32.60493Latitude: L10009614226GlobalId: LDS: QUARTERLYInspectionFrequency: EANOTIFICATIONPERMTIER: RESEARCH COMPOSTINGOPERATIONFacilityType2: ORGANIC MATERIALS HANDLINGFACILITIESFacilityType: OTAY LANDFILL, INCOperator: OTAY LANDFILL, INCOwnerName: 37-AA-0984SWISNumber: SANDIEGORegion: ACTIVEOperationalStatus: ACTIVESITESFacilityStatus: SAN DIEGO CO. LF: NotreportedOwnerEmail: NotreportedOwnerTelephone: NotreportedOwnerContact: NotreportedOwnerCity/State/Zip: NotreportedOwnerAddress: UnknownOwnerName: NotreportedOperatorEmail: NotreportedOperatorTelephone: NotreportedOperatorContact: NotreportedOperatorCity/State/Zip: NotreportedOperatorAddress: UnknownOperatorName: Detail As Of 01/2014: 230DisposalArea (Acre): Monday - Friday 7am-4pm; Saturday 7am-3pmHoursofOperation: Construction & Demolition;Green Materials;Household Trash;Metals;Tires;Waste Accepted: ActiveStatus: 24,514,904RemainingCapacity(Million): Solid WasteLandfillPresentUse: 346PermittedCapacity: N/AMaximunDepthFill(Ft): APPROPRIATE TECHNOLOGIES II INC (Continued) S109287760 TC5146125.2s Page 122 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 06/24/2013StatusDate: ActiveStatus: NotreportedApplicationFeeAmtReceived: Notreported301H: NotreportedDredgeFillFee: N - NoReclamation: NotreportedNpdesType: NotreportedMajor-Minor: NotreportedNpdes# CA#: R9-1993-086Order #: 9Region: EnrolleeRegMeasureType: 213828RegMeasureId: 9000000214WDID: 1# Of Programs: LNDISPProgramCategory2: LNDISPProgramCategory1: LFOPERProgram: NotreportedFacilityWasteType4: NotreportedFacilityWasteType3: Solid wastes, NECFacilityWasteType2: Process waste, NECFacilityWasteType: X - Facility is not aPOTWPretreatment: BComplexity: 1ThreatToWaterQuality: 0DesignFlow: RegMeasSourceOfFacility: 1# Of Places: NotreportedNAICSDesc3: NotreportedNAICSCode3: NotreportedNAICSDesc2: NotreportedNAICSCode2: NotreportedNAICSDesc1: NotreportedNAICSCode1: NotreportedSICDesc3: NotreportedSICCode3: NotreportedSICDesc2: NotreportedSICCode2: RefuseSystemsSICDesc1: 4953SICCode1: 117.01644PlaceLongitude: 32.60149PlaceLatitude: 1# Of Agencies: Privately-OwnedBusinessAgencyType: Solid Waste Class III - nonhazardous solidwastesFacilityType: LandfillPlaceSubtype: Waste ManagementUnitPlaceType: Republic Services (former Allied Waste), IncAgencyName: 246288FacilityId: 9Region: ENF: Click here to access the California GeoTracker records for this facility: see "Site Documents" tab). the San Diego Water Board web page and in the Geotracker database APPROPRIATE TECHNOLOGIES II INC (Continued)S109287760 TC5146125.2s Page 123 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedSICDesc3: NotreportedSICCode3: NotreportedSICDesc2: NotreportedSICCode2: RefuseSystemsSICDesc1: 4953SICCode1: 117.01644PlaceLongitude: 32.60149PlaceLatitude: 1# Of Agencies: Privately-OwnedBusinessAgencyType: Solid Waste Class III - nonhazardous solidwastesFacilityType: LandfillPlaceSubtype: Waste ManagementUnitPlaceType: Republic Services (former Allied Waste), IncAgencyName: 246288FacilityId: 9Region: 0Total $ Paid/Completed Amount: 0Project $ Completed: 0Liability $ Paid: 0Project $ Amount: 0Liability $ Amount: 0InitialAssessedAmount: 0TotalAssessmentAmount: 1# Of Programs1: NotreportedLatestMilestoneCompletionDate: LFOPERProgram: Region. Class III and unclassified WMUs located in the San Diego decommissioned waste (low-level radioactive wastes) at Order D-62-02 to implement a moratorium on the disposal of CAO R9-2002-330 was issued pursuant to Governor’sExecutiveDescription: Enforcement - 9000000214Title: HistoricalStatus: NotreportedEPLIssuanceDate: NotreportedACLIssuanceDate: NotreportedTerminationDate: NotreportedAchieveDate: NotreportedAdoption/Issuance Date: 10/11/2002EffectiveDate: Clean-up and AbatementOrderEnforcementActionType: R9-2002-330Order / Resolution Number: 9Region: 246812EnforcementId(EID): PassiveDirection/Voice: 17 - SiblingsiteFeeCode: IIndividual/General: YStatusEnrollee: NotreportedWDRReview - Planned: NotreportedWDRReview - Pending: NotreportedWDRReview - No Action Required: NotreportedWDRReview - Rescind: NotreportedWDRReview - Revise/Renew: NotreportedWDRReview - Amend: NotreportedTerminationDate: 06/15/2010Expiration/Review Date: 02/26/1979EffectiveDate: APPROPRIATE TECHNOLOGIES II INC (Continued)S109287760 TC5146125.2s Page 124 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedEPLIssuanceDate: NotreportedACLIssuanceDate: NotreportedTerminationDate: NotreportedAchieveDate: NotreportedAdoption/Issuance Date: 05/10/2002EffectiveDate: 13267LetterEnforcementActionType: UNKNOWNOrder / Resolution Number: 9Region: 242139EnforcementId(EID): PassiveDirection/Voice: 17 - SiblingsiteFeeCode: IIndividual/General: YStatusEnrollee: NotreportedWDRReview - Planned: NotreportedWDRReview - Pending: NotreportedWDRReview - No Action Required: NotreportedWDRReview - Rescind: NotreportedWDRReview - Revise/Renew: NotreportedWDRReview - Amend: NotreportedTerminationDate: 06/15/2010Expiration/Review Date: 02/26/1979EffectiveDate: 06/24/2013StatusDate: ActiveStatus: NotreportedApplicationFeeAmtReceived: Notreported301H: NotreportedDredgeFillFee: N - NoReclamation: NotreportedNpdesType: NotreportedMajor-Minor: NotreportedNpdes# CA#: R9-1993-086Order #: 9Region: EnrolleeRegMeasureType: 213828RegMeasureId: 9000000214WDID: 1# Of Programs: LNDISPProgramCategory2: LNDISPProgramCategory1: LFOPERProgram: NotreportedFacilityWasteType4: NotreportedFacilityWasteType3: Solid wastes, NECFacilityWasteType2: Process waste, NECFacilityWasteType: X - Facility is not aPOTWPretreatment: BComplexity: 1ThreatToWaterQuality: 0DesignFlow: RegMeasSourceOfFacility: 1# Of Places: NotreportedNAICSDesc3: NotreportedNAICSCode3: NotreportedNAICSDesc2: NotreportedNAICSCode2: NotreportedNAICSDesc1: NotreportedNAICSCode1: APPROPRIATE TECHNOLOGIES II INC (Continued)S109287760 TC5146125.2s Page 125 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation R9-1993-086Order #: 9Region: EnrolleeRegMeasureType: 213828RegMeasureId: 9000000214WDID: 1# Of Programs: LNDISPProgramCategory2: LNDISPProgramCategory1: LFOPERProgram: NotreportedFacilityWasteType4: NotreportedFacilityWasteType3: Solid wastes, NECFacilityWasteType2: Process waste, NECFacilityWasteType: X - Facility is not aPOTWPretreatment: BComplexity: 1ThreatToWaterQuality: 0DesignFlow: RegMeasSourceOfFacility: 1# Of Places: NotreportedNAICSDesc3: NotreportedNAICSCode3: NotreportedNAICSDesc2: NotreportedNAICSCode2: NotreportedNAICSDesc1: NotreportedNAICSCode1: NotreportedSICDesc3: NotreportedSICCode3: NotreportedSICDesc2: NotreportedSICCode2: RefuseSystemsSICDesc1: 4953SICCode1: 117.01644PlaceLongitude: 32.60149PlaceLatitude: 1# Of Agencies: Privately-OwnedBusinessAgencyType: Solid Waste Class III - nonhazardous solidwastesFacilityType: LandfillPlaceSubtype: Waste ManagementUnitPlaceType: Republic Services (former Allied Waste), IncAgencyName: 246288FacilityId: 9Region: 0Total $ Paid/Completed Amount: 0Project $ Completed: 0Liability $ Paid: 0Project $ Amount: 0Liability $ Amount: 0InitialAssessedAmount: 0TotalAssessmentAmount: 1# Of Programs1: 2003-01-31LatestMilestoneCompletionDate: LFOPERProgram: EXEC DIRECTOR SWRCB ON 4/25/02. CONSTITUENTS IN LEACHATE AND/OR GROUNDWATER. PER REQUEST OF REQUEST FOR ANALYTICAL RESULTS FOR RADIOACTIVEWASTEDescription: Enforcement - 9000000214Title: HistoricalStatus: APPROPRIATE TECHNOLOGIES II INC (Continued)S109287760 TC5146125.2s Page 126 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 1# Of Agencies: Privately-OwnedBusinessAgencyType: Solid Waste Class III - nonhazardous solidwastesFacilityType: LandfillPlaceSubtype: Waste ManagementUnitPlaceType: Republic Services (former Allied Waste), IncAgencyName: 246288FacilityId: 9Region: 0Total $ Paid/Completed Amount: 0Project $ Completed: 0Liability $ Paid: 0Project $ Amount: 0Liability $ Amount: 0InitialAssessedAmount: 0TotalAssessmentAmount: 1# Of Programs1: 2001-10-18LatestMilestoneCompletionDate: LFOPERProgram: include radioactive waste constituents. monitoring program for surface water and groundwater to concerning management of radioactive wastes and revised WC 13267 letter requesting amended ROWD (update to JTD)Description: Enforcement - 9000000214Title: HistoricalStatus: NotreportedEPLIssuanceDate: NotreportedACLIssuanceDate: NotreportedTerminationDate: 2001-10-18AchieveDate: NotreportedAdoption/Issuance Date: 07/02/2001EffectiveDate: 13267LetterEnforcementActionType: UNKNOWNOrder / Resolution Number: 9Region: 238569EnforcementId(EID): PassiveDirection/Voice: 17 - SiblingsiteFeeCode: IIndividual/General: YStatusEnrollee: NotreportedWDRReview - Planned: NotreportedWDRReview - Pending: NotreportedWDRReview - No Action Required: NotreportedWDRReview - Rescind: NotreportedWDRReview - Revise/Renew: NotreportedWDRReview - Amend: NotreportedTerminationDate: 06/15/2010Expiration/Review Date: 02/26/1979EffectiveDate: 06/24/2013StatusDate: ActiveStatus: NotreportedApplicationFeeAmtReceived: Notreported301H: NotreportedDredgeFillFee: N - NoReclamation: NotreportedNpdesType: NotreportedMajor-Minor: NotreportedNpdes# CA#: APPROPRIATE TECHNOLOGIES II INC (Continued)S109287760 TC5146125.2s Page 127 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 9Region: 238501EnforcementId(EID): PassiveDirection/Voice: 17 - SiblingsiteFeeCode: IIndividual/General: YStatusEnrollee: NotreportedWDRReview - Planned: NotreportedWDRReview - Pending: NotreportedWDRReview - No Action Required: NotreportedWDRReview - Rescind: NotreportedWDRReview - Revise/Renew: NotreportedWDRReview - Amend: NotreportedTerminationDate: 06/15/2010Expiration/Review Date: 02/26/1979EffectiveDate: 06/24/2013StatusDate: ActiveStatus: NotreportedApplicationFeeAmtReceived: Notreported301H: NotreportedDredgeFillFee: N - NoReclamation: NotreportedNpdesType: NotreportedMajor-Minor: NotreportedNpdes# CA#: R9-1993-086Order #: 9Region: EnrolleeRegMeasureType: 213828RegMeasureId: 9000000214WDID: 1# Of Programs: LNDISPProgramCategory2: LNDISPProgramCategory1: LFOPERProgram: NotreportedFacilityWasteType4: NotreportedFacilityWasteType3: Solid wastes, NECFacilityWasteType2: Process waste, NECFacilityWasteType: X - Facility is not aPOTWPretreatment: BComplexity: 1ThreatToWaterQuality: 0DesignFlow: RegMeasSourceOfFacility: 1# Of Places: NotreportedNAICSDesc3: NotreportedNAICSCode3: NotreportedNAICSDesc2: NotreportedNAICSCode2: NotreportedNAICSDesc1: NotreportedNAICSCode1: NotreportedSICDesc3: NotreportedSICCode3: NotreportedSICDesc2: NotreportedSICCode2: RefuseSystemsSICDesc1: 4953SICCode1: 117.01644PlaceLongitude: 32.60149PlaceLatitude: APPROPRIATE TECHNOLOGIES II INC (Continued)S109287760 TC5146125.2s Page 128 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedFacilityWasteType3: Solid wastes, NECFacilityWasteType2: Process waste, NECFacilityWasteType: X - Facility is not aPOTWPretreatment: BComplexity: 1ThreatToWaterQuality: 0DesignFlow: RegMeasSourceOfFacility: 1# Of Places: NotreportedNAICSDesc3: NotreportedNAICSCode3: NotreportedNAICSDesc2: NotreportedNAICSCode2: NotreportedNAICSDesc1: NotreportedNAICSCode1: NotreportedSICDesc3: NotreportedSICCode3: NotreportedSICDesc2: NotreportedSICCode2: RefuseSystemsSICDesc1: 4953SICCode1: 117.01644PlaceLongitude: 32.60149PlaceLatitude: 1# Of Agencies: Privately-OwnedBusinessAgencyType: Solid Waste Class III - nonhazardous solidwastesFacilityType: LandfillPlaceSubtype: Waste ManagementUnitPlaceType: Republic Services (former Allied Waste), IncAgencyName: 246288FacilityId: 9Region: 0Total $ Paid/Completed Amount: 0Project $ Completed: 0Liability $ Paid: 0Project $ Amount: 0Liability $ Amount: 0InitialAssessedAmount: 0TotalAssessmentAmount: 1# Of Programs1: NotreportedLatestMilestoneCompletionDate: LFOPERProgram: radioactive waste constituents. plan including surface and ground water discharges of low level radioactive wastes and monitoring & reporting Requested info included plans for management of existing NOV for failure to submit information under WC13267.Description: Enforcement - 9000000214Title: HistoricalStatus: NotreportedEPLIssuanceDate: NotreportedACLIssuanceDate: 10/02/2001TerminationDate: NotreportedAchieveDate: NotreportedAdoption/Issuance Date: 10/02/2001EffectiveDate: Notice ofViolationEnforcementActionType: UNKNOWNOrder / Resolution Number: APPROPRIATE TECHNOLOGIES II INC (Continued)S109287760 TC5146125.2s Page 129 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 0Project $ Completed: 0Liability $ Paid: 0Project $ Amount: 0Liability $ Amount: 0InitialAssessedAmount: 0TotalAssessmentAmount: 1# Of Programs1: 2001-10-18LatestMilestoneCompletionDate: LFOPERProgram: include radioactive waste constituents. monitoring program for surface water and groundwater to concerning management of radioactive wastes and revised WC 13267 letter requesting amended ROWD (update to JTD)Description: Enforcement - 9000000214Title: HistoricalStatus: NotreportedEPLIssuanceDate: NotreportedACLIssuanceDate: NotreportedTerminationDate: 2001-10-18AchieveDate: NotreportedAdoption/Issuance Date: 07/02/2001EffectiveDate: 13267LetterEnforcementActionType: UNKNOWNOrder / Resolution Number: 9Region: 236596EnforcementId(EID): PassiveDirection/Voice: 17 - SiblingsiteFeeCode: IIndividual/General: YStatusEnrollee: NotreportedWDRReview - Planned: NotreportedWDRReview - Pending: NotreportedWDRReview - No Action Required: NotreportedWDRReview - Rescind: NotreportedWDRReview - Revise/Renew: NotreportedWDRReview - Amend: NotreportedTerminationDate: 06/15/2010Expiration/Review Date: 02/26/1979EffectiveDate: 06/24/2013StatusDate: ActiveStatus: NotreportedApplicationFeeAmtReceived: Notreported301H: NotreportedDredgeFillFee: N - NoReclamation: NotreportedNpdesType: NotreportedMajor-Minor: NotreportedNpdes# CA#: R9-1993-086Order #: 9Region: EnrolleeRegMeasureType: 213828RegMeasureId: 9000000214WDID: 1# Of Programs: LNDISPProgramCategory2: LNDISPProgramCategory1: LFOPERProgram: NotreportedFacilityWasteType4: APPROPRIATE TECHNOLOGIES II INC (Continued)S109287760 TC5146125.2s Page 130 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedWDRReview - Revise/Renew: NotreportedWDRReview - Amend: NotreportedTerminationDate: 06/15/2010Expiration/Review Date: 02/26/1979EffectiveDate: 06/24/2013StatusDate: ActiveStatus: NotreportedApplicationFeeAmtReceived: Notreported301H: NotreportedDredgeFillFee: N - NoReclamation: NotreportedNpdesType: NotreportedMajor-Minor: NotreportedNpdes# CA#: R9-1993-086Order #: 9Region: EnrolleeRegMeasureType: 213828RegMeasureId: 9000000214WDID: 1# Of Programs: LNDISPProgramCategory2: LNDISPProgramCategory1: LFOPERProgram: NotreportedFacilityWasteType4: NotreportedFacilityWasteType3: Solid wastes, NECFacilityWasteType2: Process waste, NECFacilityWasteType: X - Facility is not aPOTWPretreatment: BComplexity: 1ThreatToWaterQuality: 0DesignFlow: RegMeasSourceOfFacility: 1# Of Places: NotreportedNAICSDesc3: NotreportedNAICSCode3: NotreportedNAICSDesc2: NotreportedNAICSCode2: NotreportedNAICSDesc1: NotreportedNAICSCode1: NotreportedSICDesc3: NotreportedSICCode3: NotreportedSICDesc2: NotreportedSICCode2: RefuseSystemsSICDesc1: 4953SICCode1: 117.01644PlaceLongitude: 32.60149PlaceLatitude: 1# Of Agencies: Privately-OwnedBusinessAgencyType: Solid Waste Class III - nonhazardous solidwastesFacilityType: LandfillPlaceSubtype: Waste ManagementUnitPlaceType: Republic Services (former Allied Waste), IncAgencyName: 246288FacilityId: 9Region: 0Total $ Paid/Completed Amount: APPROPRIATE TECHNOLOGIES II INC (Continued)S109287760 TC5146125.2s Page 131 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedNAICSCode3: NotreportedNAICSDesc2: NotreportedNAICSCode2: NotreportedNAICSDesc1: NotreportedNAICSCode1: NotreportedSICDesc3: NotreportedSICCode3: NotreportedSICDesc2: NotreportedSICCode2: RefuseSystemsSICDesc1: 4953SICCode1: 117.01644PlaceLongitude: 32.60149PlaceLatitude: 1# Of Agencies: Privately-OwnedBusinessAgencyType: Solid Waste Class III - nonhazardous solidwastesFacilityType: LandfillPlaceSubtype: Waste ManagementUnitPlaceType: Republic Services (former Allied Waste), IncAgencyName: 246288FacilityId: 9Region: 0Total $ Paid/Completed Amount: 0Project $ Completed: 0Liability $ Paid: 0Project $ Amount: 0Liability $ Amount: 0InitialAssessedAmount: 0TotalAssessmentAmount: 1# Of Programs1: NotreportedLatestMilestoneCompletionDate: LFOPERProgram: health effects. and State DHS are also evaluating the potential human Otay Annex (Class III) Landfill. County of San Diego LEA quality from low level radioactive wastes discovered at the Letter requesting information to assess the threat towaterDescription: Enforcement - 9000000214Title: HistoricalStatus: NotreportedEPLIssuanceDate: NotreportedACLIssuanceDate: NotreportedTerminationDate: 2000-12-28AchieveDate: NotreportedAdoption/Issuance Date: 11/14/2000EffectiveDate: 13267LetterEnforcementActionType: UNKNOWNOrder / Resolution Number: 9Region: 235172EnforcementId(EID): PassiveDirection/Voice: 17 - SiblingsiteFeeCode: IIndividual/General: YStatusEnrollee: NotreportedWDRReview - Planned: NotreportedWDRReview - Pending: NotreportedWDRReview - No Action Required: NotreportedWDRReview - Rescind: APPROPRIATE TECHNOLOGIES II INC (Continued)S109287760 TC5146125.2s Page 132 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation excess leachate production (approx. 900,000 gal/month) and Investigative Order and NOV requesting informationaboutDescription: Inc 13267 Letter R9-2016-0067 for Republic Services (former Allied Waste),Title: ActiveStatus: NotreportedEPLIssuanceDate: NotreportedACLIssuanceDate: NotreportedTerminationDate: NotreportedAchieveDate: 07/11/2016Adoption/Issuance Date: 07/11/2016EffectiveDate: 13267LetterEnforcementActionType: R9-2016-0067Order / Resolution Number: 9Region: 406715EnforcementId(EID): PassiveDirection/Voice: 50 - Land Disposal Site paying tippingfeeFeeCode: IIndividual/General: NStatusEnrollee: NotreportedWDRReview - Planned: NotreportedWDRReview - Pending: NotreportedWDRReview - No Action Required: NotreportedWDRReview - Rescind: 11/3/2003WDRReview - Revise/Renew: NotreportedWDRReview - Amend: NotreportedTerminationDate: 06/30/2010Expiration/Review Date: 10/15/1997EffectiveDate: 12/11/2014StatusDate: ActiveStatus: NotreportedApplicationFeeAmtReceived: Notreported301H: NotreportedDredgeFillFee: N - NoReclamation: NotreportedNpdesType: NotreportedMajor-Minor: NotreportedNpdes# CA#: R9-1990-0009Order #: 9Region: WDRRegMeasureType: 131120RegMeasureId: 9000000214WDID: 1# Of Programs: LNDISPProgramCategory2: LNDISPProgramCategory1: LFOPERProgram: NotreportedFacilityWasteType4: NotreportedFacilityWasteType3: NotreportedFacilityWasteType2: Solid wastes, NECFacilityWasteType: X - Facility is not aPOTWPretreatment: BComplexity: 1ThreatToWaterQuality: 0DesignFlow: RegMeasSourceOfFacility: 1# Of Places: NotreportedNAICSDesc3: APPROPRIATE TECHNOLOGIES II INC (Continued)S109287760 TC5146125.2s Page 133 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedNpdesType: NotreportedMajor-Minor: NotreportedNpdes# CA#: R9-1990-0009Order #: 9Region: WDRRegMeasureType: 131120RegMeasureId: 9000000214WDID: 1# Of Programs: LNDISPProgramCategory2: LNDISPProgramCategory1: LFOPERProgram: NotreportedFacilityWasteType4: NotreportedFacilityWasteType3: NotreportedFacilityWasteType2: Solid wastes, NECFacilityWasteType: X - Facility is not aPOTWPretreatment: BComplexity: 1ThreatToWaterQuality: 0DesignFlow: RegMeasSourceOfFacility: 1# Of Places: NotreportedNAICSDesc3: NotreportedNAICSCode3: NotreportedNAICSDesc2: NotreportedNAICSCode2: NotreportedNAICSDesc1: NotreportedNAICSCode1: NotreportedSICDesc3: NotreportedSICCode3: NotreportedSICDesc2: NotreportedSICCode2: RefuseSystemsSICDesc1: 4953SICCode1: 117.01644PlaceLongitude: 32.60149PlaceLatitude: 1# Of Agencies: Privately-OwnedBusinessAgencyType: Solid Waste Class III - nonhazardous solidwastesFacilityType: LandfillPlaceSubtype: Waste ManagementUnitPlaceType: Republic Services (former Allied Waste), IncAgencyName: 246288FacilityId: 9Region: 0Total $ Paid/Completed Amount: 0Project $ Completed: 0Liability $ Paid: 0Project $ Amount: 0Liability $ Amount: 0InitialAssessedAmount: 0TotalAssessmentAmount: 1# Of Programs1: NotreportedLatestMilestoneCompletionDate: LFOPERProgram: leachate ponding seems to be occurring. slope stability evaluation for SE corner of landfill where APPROPRIATE TECHNOLOGIES II INC (Continued)S109287760 TC5146125.2s Page 134 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedSICDesc2: NotreportedSICCode2: RefuseSystemsSICDesc1: 4953SICCode1: 117.01644PlaceLongitude: 32.60149PlaceLatitude: 1# Of Agencies: Privately-OwnedBusinessAgencyType: Solid Waste Class III - nonhazardous solidwastesFacilityType: LandfillPlaceSubtype: Waste ManagementUnitPlaceType: Republic Services (former Allied Waste), IncAgencyName: 246288FacilityId: 9Region: 0Total $ Paid/Completed Amount: 0Project $ Completed: 0Liability $ Paid: 0Project $ Amount: 0Liability $ Amount: 0InitialAssessedAmount: 0TotalAssessmentAmount: 1# Of Programs1: NotreportedLatestMilestoneCompletionDate: LFOPERProgram: NotreportedDescription: NOV R9-2016-0067 for Republic Services (former Allied Waste), IncTitle: ActiveStatus: NotreportedEPLIssuanceDate: NotreportedACLIssuanceDate: NotreportedTerminationDate: NotreportedAchieveDate: 07/11/2016Adoption/Issuance Date: 07/11/2016EffectiveDate: Notice ofViolationEnforcementActionType: R9-2016-0067Order / Resolution Number: 9Region: 404725EnforcementId(EID): PassiveDirection/Voice: 50 - Land Disposal Site paying tippingfeeFeeCode: IIndividual/General: NStatusEnrollee: NotreportedWDRReview - Planned: NotreportedWDRReview - Pending: NotreportedWDRReview - No Action Required: NotreportedWDRReview - Rescind: 11/3/2003WDRReview - Revise/Renew: NotreportedWDRReview - Amend: NotreportedTerminationDate: 06/30/2010Expiration/Review Date: 10/15/1997EffectiveDate: 12/11/2014StatusDate: ActiveStatus: NotreportedApplicationFeeAmtReceived: Notreported301H: NotreportedDredgeFillFee: N - NoReclamation: APPROPRIATE TECHNOLOGIES II INC (Continued)S109287760 TC5146125.2s Page 135 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 12/10/2014TerminationDate: NotreportedAchieveDate: 12/10/2014Adoption/Issuance Date: 12/10/2014EffectiveDate: Staff EnforcementLetterEnforcementActionType: NotreportedOrder / Resolution Number: 9Region: 399098EnforcementId(EID): PassiveDirection/Voice: 50 - Land Disposal Site paying tippingfeeFeeCode: IIndividual/General: NStatusEnrollee: NotreportedWDRReview - Planned: NotreportedWDRReview - Pending: NotreportedWDRReview - No Action Required: NotreportedWDRReview - Rescind: 11/3/2003WDRReview - Revise/Renew: NotreportedWDRReview - Amend: NotreportedTerminationDate: 06/30/2010Expiration/Review Date: 10/15/1997EffectiveDate: 12/11/2014StatusDate: ActiveStatus: NotreportedApplicationFeeAmtReceived: Notreported301H: NotreportedDredgeFillFee: N - NoReclamation: NotreportedNpdesType: NotreportedMajor-Minor: NotreportedNpdes# CA#: R9-1990-0009Order #: 9Region: WDRRegMeasureType: 131120RegMeasureId: 9000000214WDID: 1# Of Programs: LNDISPProgramCategory2: LNDISPProgramCategory1: LFOPERProgram: NotreportedFacilityWasteType4: NotreportedFacilityWasteType3: NotreportedFacilityWasteType2: Solid wastes, NECFacilityWasteType: X - Facility is not aPOTWPretreatment: BComplexity: 1ThreatToWaterQuality: 0DesignFlow: RegMeasSourceOfFacility: 1# Of Places: NotreportedNAICSDesc3: NotreportedNAICSCode3: NotreportedNAICSDesc2: NotreportedNAICSCode2: NotreportedNAICSDesc1: NotreportedNAICSCode1: NotreportedSICDesc3: NotreportedSICCode3: APPROPRIATE TECHNOLOGIES II INC (Continued)S109287760 TC5146125.2s Page 136 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 01/19/2004ClosureEstablishedA: 11/26/2008CostAnniversary: NotreportedLiabilityMechanismB: 01/01/2004LiabilityEstablishedA: INSURANCELiabilityMechanismA: 424,860.00CorrectiveActionPlanEstimate: 06/01/2017CorrectiveActionInflationdate: 430,383.00CorrectiveActionInflationEstimate: YesCorrectiveActionApproved: 446,503.00CorrectiveActiontCoverage: 01/19/2004CorrectiveActionExtablishedA: NotreportedPostClosureAdequacy: 17,794,713.00PostClosureCoverate: NotreportedPostClosureMechanismB: 01/19/2004PostClosureEstablishedA: SURETYBONDPostClosureMechanismA: 12,707,139.00ClosureInflationEstimate: NotreportedClosureAdequacy: 12,707,139.00ClosureCoverage: NotreportedClosureMechanismB: SURETYBONDClosureMechanismA: 06/09/2017Review: YesLiaApproved: 10,000,000.00LiaCoverage: 12/31/2016CorActPlanDate: 424,860.00CorActPlanCoverage: 430,383.00CorActInfCoverage: NotreportedCorActMecAdequacyDate: YesCorActApproved: 446,503.00CorActCoverage: 06/01/2017PostCloseInfCoverageDate: 17,794,713.00PostCloseInfCoverage: 06/01/2016PostCloseAdequacyDate: YesPostCloseApproved: 06/01/2016ClosurePlanDate: 12,544,066.00ClosurePlanCoverage: 06/01/2017ClosureInfCoverageDate: YesClosureApproved: 37-AA-0010SWIS_NO: 2Region: CA Financial Assurance 2: 0Total $ Paid/Completed Amount: 0Project $ Completed: 0Liability $ Paid: 0Project $ Amount: 0Liability $ Amount: 0InitialAssessedAmount: 0TotalAssessmentAmount: 1# Of Programs1: NotreportedLatestMilestoneCompletionDate: LFOPERProgram: NotreportedDescription: SEL 12/10/2014 for Republic Services (former Allied Waste), IncTitle: HistoricalStatus: NotreportedEPLIssuanceDate: NotreportedACLIssuanceDate: APPROPRIATE TECHNOLOGIES II INC (Continued)S109287760 TC5146125.2s Page 137 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedDEVELOPERCITY: NotreportedDEVELOPERADDRESS: NotreportedDEVELOPERNAME: NotreportedOPERATORTYPE: NotreportedOPERATORCONTACTEMAIL: NotreportedOPERATORCONTACTPHONEEXT: NotreportedOPERATORCONTACTPHONE: NotreportedOPERATORCONTACTTITLE: NotreportedOPERATORCONTACTNAME: NotreportedOPERATORZIP: NotreportedOPERATORSTATE: NotreportedOPERATORCITY: NotreportedOPERATORADDRESS: NotreportedOPERATORNAME: NotreportedFACILITYCONTACTEMAIL: NotreportedFACILITYCONTACTPHONEEXT: NotreportedFACILITYCONTACTPHONE: NotreportedFACILITYCONTACTTITLE: NotreportedFACILITYCONTACTNAME: NotreportedPLACESIZEUNIT: NotreportedPLACESIZE: NotreportedSTATUSDATE: NotreportedSTATUSCODENAME: NotreportedPROCESSEDDATE: NotreportedRECEIVEDDATE: 92071DischargeZip: CaliforniaDischargeState: SanteeDischargeCity: 8514 MastBlvdDischargeAddress: Otay LandfillIncDischargeName: NotreportedTerminationDateOfRegulatoryMeasure: NotreportedExpirationDateOfRegulatoryMeasure: 11/10/1997EffectiveDateOfRegulatoryMeasure: NotreportedAdoptionDateOfRegulatoryMeasure: IndustrialProgramType: 937I013509WDID: NotreportedPlaceId: EnrolleeRegulatoryMeasureType: 97-03-DWQOrderNo: 218578RegulatoryMeasureId: 9Region: 0AgencyId: ActiveFacilityStatus: CAS000001NpdesNumber: NPDES: NotreportedContact: NotreportedLiabilityAdequacy: NotreportedLiabilityEstabllishedB: 0CorrectiveActiontDisbursement: NotreportedCorrectiveActionExtablishedB: NotreportedCorrectiveActionMechanismB: SURETYBONDCorrectiveActionMechanismA: 0PostClosureDisbursement: NotreportedPostClosureEstablishedB: 0ClosureDisbursement: NotreportedClosureEstablishedB: APPROPRIATE TECHNOLOGIES II INC (Continued)S109287760 TC5146125.2s Page 138 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation AcresPLACESIZEUNIT: 516PLACESIZE: 11/10/1997STATUSDATE: ActiveSTATUSCODENAME: 11/10/1997PROCESSEDDATE: 05/09/2008RECEIVEDDATE: NotreportedDischargeZip: NotreportedDischargeState: NotreportedDischargeCity: NotreportedDischargeAddress: NotreportedDischargeName: NotreportedTerminationDateOfRegulatoryMeasure: NotreportedExpirationDateOfRegulatoryMeasure: NotreportedEffectiveDateOfRegulatoryMeasure: NotreportedAdoptionDateOfRegulatoryMeasure: NotreportedProgramType: 937I013509WDID: NotreportedPlaceId: IndustrialRegulatoryMeasureType: NotreportedOrderNo: 218578RegulatoryMeasureId: 9Region: NotreportedAgencyId: NotreportedFacilityStatus: NotreportedNpdesNumber: NotreportedTERTIARYSIC: NotreportedSECONDARYSIC: NotreportedPRIMARYSIC: NotreportedCERTIFICATIONDATE: NotreportedCERTIFIERTITLE: NotreportedCERTIFIERNAME: NotreportedRECEIVINGWATERNAME: NotreportedDIRDISCHARGEUSWATERIND: NotreportedCONSTYPEWATERSEWERIND: NotreportedCONSTYPEUTILITYIND: NotreportedCONSTYPEUTILITYDESCRIPTION: NotreportedCONSTYPETRANSPORTIND: NotreportedCONSTYPERESIDENTIALIND: NotreportedCONSTYPERECONSIND: NotreportedCONSTYPEOTHERIND: NotreportedCONSTYPEOTHERDESRIPTION: NotreportedCONSTYPEINDUSTRIALIND: NotreportedCONSTYPEGASLINEIND: NotreportedCONSTYPEELECTRICALLINEIND: NotreportedCONSTYPECOMMERTIALIND: NotreportedCONSTYPECOMMLINEIND: NotreportedCONSTYPECABLELINEIND: NotreportedCONSTYPEBELOWGROUNDIND: NotreportedCONSTYPEABOVEGROUNDIND: NotreportedEMERGENCYPHONEEXT: NotreportedEMERGENCYPHONENO: NotreportedCONSTYPELINEARUTILITYIND: NotreportedDEVELOPERCONTACTTITLE: NotreportedDEVELOPERCONTACTNAME: NotreportedDEVELOPERZIP: NotreportedDEVELOPERSTATE: APPROPRIATE TECHNOLOGIES II INC (Continued)S109287760 TC5146125.2s Page 139 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedTERTIARYSIC: NotreportedSECONDARYSIC: 4953-RefuseSystemsPRIMARYSIC: 04-MAY-15CERTIFICATIONDATE: GeneralManagerCERTIFIERTITLE: NeilMohrCERTIFIERNAME: Otay Valley River ToPacificRECEIVINGWATERNAME: NDIRDISCHARGEUSWATERIND: NotreportedCONSTYPEWATERSEWERIND: NotreportedCONSTYPEUTILITYIND: NotreportedCONSTYPEUTILITYDESCRIPTION: NotreportedCONSTYPETRANSPORTIND: NotreportedCONSTYPERESIDENTIALIND: NotreportedCONSTYPERECONSIND: NotreportedCONSTYPEOTHERIND: NotreportedCONSTYPEOTHERDESRIPTION: NotreportedCONSTYPEINDUSTRIALIND: NotreportedCONSTYPEGASLINEIND: NotreportedCONSTYPEELECTRICALLINEIND: NotreportedCONSTYPECOMMERTIALIND: NotreportedCONSTYPECOMMLINEIND: NotreportedCONSTYPECABLELINEIND: NotreportedCONSTYPEBELOWGROUNDIND: NotreportedCONSTYPEABOVEGROUNDIND: 14EMERGENCYPHONEEXT: 619-449-9579EMERGENCYPHONENO: NotreportedCONSTYPELINEARUTILITYIND: NotreportedDEVELOPERCONTACTTITLE: NotreportedDEVELOPERCONTACTNAME: NotreportedDEVELOPERZIP: CaliforniaDEVELOPERSTATE: NotreportedDEVELOPERCITY: NotreportedDEVELOPERADDRESS: NotreportedDEVELOPERNAME: PrivateBusinessOPERATORTYPE: agunner@republicservices.comOPERATORCONTACTEMAIL: NotreportedOPERATORCONTACTPHONEEXT: 619-499-9579OPERATORCONTACTPHONE: EnvironmentalSpecialistOPERATORCONTACTTITLE: AntoniaGunnerOPERATORCONTACTNAME: 92071OPERATORZIP: CaliforniaOPERATORSTATE: SanteeOPERATORCITY: 8514 MastBlvdOPERATORADDRESS: Otay LandfillIncOPERATORNAME: agunner@republicservices.comFACILITYCONTACTEMAIL: NotreportedFACILITYCONTACTPHONEEXT: 619-499-9579FACILITYCONTACTPHONE: EnvironmentalSpecialistFACILITYCONTACTTITLE: AntoniaGunnerFACILITYCONTACTNAME: APPROPRIATE TECHNOLOGIES II INC (Continued) S109287760 TC5146125.2s Page 140 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation Date Started: DISCOVERYAction: CERCLIS-NFRAP Assessment History: RCRA Deferral - LeadConfirmedDescription: Program Priority: CA NotreportedAliasAddress: APTECIIAliasName: CA NotreportedAliasAddress: OTAYLDFLAliasName: CA NotreportedAliasAddress: BKKCORPAliasName: CA NotreportedAliasAddress: OTAY IND WASTE TRANSFER STABKKAliasName: CA NotreportedAliasAddress: CHANCELLONTOGDENAliasName: CERCLIS-NFRAP Site Alias Name(s): 13004003.00000PersonID: 13301884.00000ContactSequenceID: 13003858.00000PersonID: 13296026.00000ContactSequenceID: 13003854.00000PersonID: 13290431.00000ContactSequenceID: CERCLIS-NFRAP Site Contact Details: Deferred toRCRANonNPLStatus: Not on theNPLNPLStatus: Not a FederalFacilityFederalFacility: 0902662SiteID: Following information was gathered from the prior CERCLIS update completed in 10/2013: Deferred toRCRANonNPLStatus: Not on theNPLNPL: NFederalFacility: CAT080010101EPAID: 902662SiteID: SEMS-ARCHIVE: NY MANIFEST 4792 ft.2020 CORACTIONSite4of4inclusterI 0.908 mi.RCRA-SQG Relative: Higher Actual: 349 ft. 1/2-1 RCRA-TSDFCHULAVISTA, CA 92011 ENE CORRACTS1700MAXWELLRD CAT080010101 I31 SEMS-ARCHIVEAPPROPRIATETECHNOLOGIESII 1000367959 TC5146125.2s Page 141 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation General Freight Trucking, Local General Freight Trucking, Local 4841148411NAICSCode(s): Migration of Contaminated Groundwater Under Control has been verified CA750YE - Migration of Contaminated Groundwater under Control, Yes,Action: 20101208ActualDate: ENTIREFACILITYAreaName: 09EPARegion: CAT080010101EPAID: NotreportedScheduleenddate: 20121002Originalscheduledate: General Freight Trucking, Local General Freight Trucking, Local 4841148411NAICSCode(s): CA800YEAction: 20121002ActualDate: ENTIREFACILITYAreaName: 09EPARegion: CAT080010101EPAID: NotreportedScheduleenddate: NotreportedOriginalscheduledate: General Freight Trucking, Local General Freight Trucking, Local 4841148411NAICSCode(s): CA140 - RFI Workplan Notice Of DeficiencyIssuedAction: 19940401ActualDate: WASHOUT PIT & OLD UNLINED EFFLUENTPIPESAreaName: 09EPARegion: CAT080010101EPAID: CORRACTS: NotreportedPriorityLevel: 01/23/96DateCompleted: Date Started: ARCHIVESITEAction: NotreportedPriorityLevel: 09/15/89DateCompleted: Date Started: RESOURCE CONSERVATION AND RECOVERY ACT FACILITYASSESSMENTAction: Deferred to RCRA (Subtitle C)Priority Level: 09/15/89DateCompleted: Date Started: SITEINSPECTIONAction: Deferred to RCRA (Subtitle C)Priority Level: 11/01/87DateCompleted: 03/01/84DateStarted: PRELIMINARYASSESSMENTAction: NotreportedPriorityLevel: 08/01/80DateCompleted: APPROPRIATE TECHNOLOGIES II (Continued) 1000367959 TC5146125.2s Page 142 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation General Freight Trucking, Local 4841148411NAICSCode(s): Migration of Contaminated Groundwater Under Control has been verified CA750YE - Migration of Contaminated Groundwater under Control, Yes,Action: 20110920ActualDate: ENTIREFACILITYAreaName: 09EPARegion: CAT080010101EPAID: NotreportedScheduleenddate: NotreportedOriginalscheduledate: General Freight Trucking, Local General Freight Trucking, Local 4841148411NAICSCode(s): corrective action priority CA075LO - CA Prioritization, Facility or area was assigned alowAction: 19910420ActualDate: WASHOUT PIT & OLD UNLINED EFFLUENTPIPESAreaName: 09EPARegion: CAT080010101EPAID: NotreportedScheduleenddate: NotreportedOriginalscheduledate: General Freight Trucking, Local General Freight Trucking, Local 4841148411NAICSCode(s): CA150 - RFI WorkplanApprovedAction: 19940614ActualDate: WASHOUT PIT & OLD UNLINED EFFLUENTPIPESAreaName: 09EPARegion: CAT080010101EPAID: NotreportedScheduleenddate: 20100812Originalscheduledate: General Freight Trucking, Local General Freight Trucking, Local 4841148411NAICSCode(s): Exposures Under Control has been verified CA725YE - Current Human Exposures Under Control, Yes, CurrentHumanAction: 20100812ActualDate: ENTIREFACILITYAreaName: 09EPARegion: CAT080010101EPAID: NotreportedScheduleenddate: 20101208Originalscheduledate: General Freight Trucking, Local General Freight Trucking, Local 4841148411NAICSCode(s): CA550RCAction: 20101208ActualDate: ENTIREFACILITYAreaName: 09EPARegion: CAT080010101EPAID: NotreportedScheduleenddate: 20101208Originalscheduledate: APPROPRIATE TECHNOLOGIES II (Continued) 1000367959 TC5146125.2s Page 143 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation General Freight Trucking, Local 4841148411NAICSCode(s): CA070YE - RFA Determination Of Need For An RFI, RFI isNecessaryAction: 19890527ActualDate: WASHOUT PIT & OLD UNLINED EFFLUENTPIPESAreaName: 09EPARegion: CAT080010101EPAID: NotreportedScheduleenddate: NotreportedOriginalscheduledate: General Freight Trucking, Local General Freight Trucking, Local 4841148411NAICSCode(s): stabilization evaluation CA100DC - RFI Imposition, Focused data collection requiredforAction: 19930624ActualDate: WASHOUT PIT & OLD UNLINED EFFLUENTPIPESAreaName: 09EPARegion: CAT080010101EPAID: NotreportedScheduleenddate: NotreportedOriginalscheduledate: General Freight Trucking, Local General Freight Trucking, Local 4841148411NAICSCode(s): CA200 - RFIApprovedAction: 19950222ActualDate: WASHOUT PIT & OLD UNLINED EFFLUENTPIPESAreaName: 09EPARegion: CAT080010101EPAID: NotreportedScheduleenddate: 20111124Originalscheduledate: General Freight Trucking, Local General Freight Trucking, Local 4841148411NAICSCode(s): CA550RCAction: 20110920ActualDate: ENTIREFACILITYAreaName: 09EPARegion: CAT080010101EPAID: NotreportedScheduleenddate: 20111124Originalscheduledate: General Freight Trucking, Local General Freight Trucking, Local 4841148411NAICSCode(s): Exposures Under Control has been verified CA725YE - Current Human Exposures Under Control, Yes, CurrentHumanAction: 20110920ActualDate: ENTIREFACILITYAreaName: 09EPARegion: CAT080010101EPAID: NotreportedScheduleenddate: 20111124Originalscheduledate: General Freight Trucking, Local APPROPRIATE TECHNOLOGIES II (Continued) 1000367959 TC5146125.2s Page 144 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation CAT080010101EPAID: NotreportedScheduleenddate: 19920928Originalscheduledate: General Freight Trucking, Local General Freight Trucking, Local 4841148411NAICSCode(s): considerations corrective action work at the facility, or other, administrative facility, the degree of risk, timing considerations, the status of IN). Reasons for this conclusion may be the status of, closure at the inappropriate (NF) or (2) there is a lack of technical, information other than (1) it appears to be technically, infeasible or amenable to stabilization activity at the, present time for reasons CA225NR - Stabilization Measures Evaluation, This facility is, notAction: 19920928ActualDate: WASHOUT PIT & OLD UNLINED EFFLUENTPIPESAreaName: 09EPARegion: CAT080010101EPAID: NotreportedScheduleenddate: NotreportedOriginalscheduledate: General Freight Trucking, Local General Freight Trucking, Local 4841148411NAICSCode(s): corrective action priority CA075LO - CA Prioritization, Facility or area was assigned alowAction: 19920928ActualDate: WASHOUT PIT & OLD UNLINED EFFLUENTPIPESAreaName: 09EPARegion: CAT080010101EPAID: NotreportedScheduleenddate: 19890527Originalscheduledate: General Freight Trucking, Local General Freight Trucking, Local 4841148411NAICSCode(s): CA050 - RFACompletedAction: 19890527ActualDate: WASHOUT PIT & OLD UNLINED EFFLUENTPIPESAreaName: 09EPARegion: CAT080010101EPAID: NotreportedScheduleenddate: NotreportedOriginalscheduledate: General Freight Trucking, Local General Freight Trucking, Local 4841148411NAICSCode(s): CA050RF - RFA Completed, Assessment was anRFAAction: 19890527ActualDate: WASHOUT PIT & OLD UNLINED EFFLUENTPIPESAreaName: 09EPARegion: CAT080010101EPAID: NotreportedScheduleenddate: 19890527Originalscheduledate: General Freight Trucking, Local APPROPRIATE TECHNOLOGIES II (Continued) 1000367959 TC5146125.2s Page 145 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation Facility is not located on Indian land. Additional information is not known.Land type: 09EPARegion: NotreportedContactemail: 319Telephoneext.: 626-965-0911Contacttelephone: USContactcountry: Not reported NotreportedContactaddress: JOHNFAULKNERContact: WEST COVINA, CA 91792 2210 SOUTH AZUSAAVEMailingaddress: CAT080010101EPAID: CHULA VISTA, CA 91911 1700 MAXWELLRDFacilityaddress: APPROPRIATE TECHNOLOGIES II, INC.Site name: APPROPRIATE TECHNOLOGIES II INC.Facility name: 03/04/1999Dateformreceivedbyagency: RCRA-TSDF: NotreportedScheduleenddate: 19910629Originalscheduledate: General Freight Trucking, Local General Freight Trucking, Local 4841148411NAICSCode(s): CA050 - RFACompletedAction: 19910629ActualDate: WASHOUT PIT & OLD UNLINED EFFLUENTPIPESAreaName: 09EPARegion: CAT080010101EPAID: NotreportedScheduleenddate: 19910629Originalscheduledate: General Freight Trucking, Local General Freight Trucking, Local 4841148411NAICSCode(s): CA070YE - RFA Determination Of Need For An RFI, RFI isNecessaryAction: 19910629ActualDate: WASHOUT PIT & OLD UNLINED EFFLUENTPIPESAreaName: 09EPARegion: CAT080010101EPAID: NotreportedScheduleenddate: NotreportedOriginalscheduledate: General Freight Trucking, Local General Freight Trucking, Local 4841148411NAICSCode(s): considerations corrective action work at the facility, or other, administrative facility, the degree of risk, timing considerations, the status of IN). Reasons for this conclusion may be the status of, closure at the inappropriate (NF) or (2) there is a lack of technical, information other than (1) it appears to be technically, infeasible or amenable to stabilization activity at the, present time for reasons CA225NR - Stabilization Measures Evaluation, This facility is, notAction: 19920928ActualDate: WASHOUT PIT & OLD UNLINED EFFLUENTPIPESAreaName: 09EPARegion: APPROPRIATE TECHNOLOGIES II (Continued) 1000367959 TC5146125.2s Page 146 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation PA OR CERCLAINSPECTIONEvent: 11/01/1987Eventdate: CA PRIORITIZATION-LOW CAPRIORITYEvent: 11/01/1987Eventdate: Corrective Action Summary: Large QuantityGeneratorClassification: APPROPRIATE TECHNOLOGIES II INC.Site name: 08/18/1980Dateformreceivedbyagency: Large QuantityGeneratorClassification: APPROPRIATE TECHNOLOGIESIISitename: 04/16/1990Dateformreceivedbyagency: Large QuantityGeneratorClassification: APPROPRIATE TECHNOLOGIESIISitename: 03/16/1992Dateformreceivedbyagency: Large QuantityGeneratorClassification: APPROPRIATE TECHNOLOGIES 11, INC.Site name: 03/30/1994Dateformreceivedbyagency: Large QuantityGeneratorClassification: APPROPRIATE TECHNOLOGIES IIINCSitename: 02/27/1996Dateformreceivedbyagency: Small QuantityGeneratorClassification: APPROPRIATE TECHNOLOGIES II INC.Site name: 09/01/1996Dateformreceivedbyagency: Large QuantityGeneratorClassification: APPROPRIATE TECHNOLOGIES II INC.Site name: 09/01/1996Dateformreceivedbyagency: Historical Generators: NoUsedoiltransporter: NoUsedoiltransferfacility: NoUsedoilSpecificationmarketer: NoUsedoilfuelmarketertoburner: NoUseroilrefiner: NoUsedoilprocessor: NoUsedoilfuelburner: NoFurnaceexemption: NoOn-site burner exemption: NoUndergroundinjectionactivity: YesTreater, storer or disposer of HW: NoTransporterofhazardouswaste: NoRecyclerofhazardouswaste: NoMixedwaste (haz. and radioactive): NoU.S. importer of hazardous waste: Handler Activities Summary: waste Handler is engaged in the treatment, storage or disposal ofhazardousDescription: TSDFClassification: APPROPRIATE TECHNOLOGIES II (Continued) 1000367959 TC5146125.2s Page 147 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation RELEASE TO GW CONTROLLED DETERMINATION-YES, APPLICABLE AS OF THISDATEEvent: 12/08/2010Eventdate: DATE HUMAN EXPOSURES CONTROLLED DETERMINATION-YES, APPLICABLE AS OFTHISEvent: 08/12/2010Eventdate: DATE HUMAN EXPOSURES CONTROLLED DETERMINATION-YES, APPLICABLE AS OFTHISEvent: 08/12/2010Eventdate: INVESTIGATIONCOMPLETEEvent: 02/22/1995Eventdate: INVESTIGATION WORKPLANAPPROVEDEvent: 06/14/1994Eventdate: INVESTIGATION WORKPLAN NOTICE OF DEFICIENCYISSUEDEvent: 04/01/1994Eventdate: RFI IMPOSITION-FOCUSED DATA COLLECTION REQ STABEVALEvent: 06/24/1993Eventdate: STABILIZATION STABILIZATION MEASURES EVALUATION-FACILITY NOT AMENABLETOEvent: 09/28/1992Eventdate: STABILIZATION STABILIZATION MEASURES EVALUATION-FACILITY NOT AMENABLETOEvent: 09/28/1992Eventdate: CA PRIORITIZATION-LOW CAPRIORITYEvent: 09/28/1992Eventdate: DETERMINATION OF NEED FOR AN INVESTIGATION-INVESTIGATION ISNECESSARYEvent: 06/29/1991Eventdate: RFACOMPLETEDEvent: 06/29/1991Eventdate: CA PRIORITIZATION-LOW CAPRIORITYEvent: 04/20/1991Eventdate: PA OR CERCLAINSPECTIONEvent: 09/15/1989Eventdate: DETERMINATION OF NEED FOR AN INVESTIGATION-INVESTIGATION ISNECESSARYEvent: 05/27/1989Eventdate: RFA COMPLETED-ASSESSMENT WAS ARFAEvent: 05/27/1989Eventdate: RFACOMPLETEDEvent: 05/27/1989Eventdate: LEAD AGENCYDETERMINATIONEvent: 11/01/1987Eventdate: APPROPRIATE TECHNOLOGIES II (Continued) 1000367959 TC5146125.2s Page 148 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation WRITTEN INFORMALEnforcementaction: EPAViolationleadagency: 11/29/1995Dateachievedcompliance: 11/29/1995Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 264.70-77.ERegulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: EPAEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 07/26/1996Enforcementactiondate: WRITTEN INFORMALEnforcementaction: EPAViolationleadagency: 11/29/1995Dateachievedcompliance: 11/29/1995Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 264.30-37.CRegulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: EPAEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 07/26/1996Enforcementactiondate: WRITTEN INFORMALEnforcementaction: EPAViolationleadagency: 11/29/1995Dateachievedcompliance: 11/29/1995Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 270Regulationviolated: Facility Has Received Notices of Violations: READY FOR ANTICIPATED USE DETERMINATION - READY FOR ANTICIPATEDUSEEvent: 10/02/2012Eventdate: DATE HUMAN EXPOSURES CONTROLLED DETERMINATION-YES, APPLICABLE AS OFTHISEvent: 09/20/2011Eventdate: RELEASE TO GW CONTROLLED DETERMINATION-YES, APPLICABLE AS OF THISDATEEvent: 09/20/2011Eventdate: REMEDY CONSTRUCTION-REMEDYCONSTRUCTEDEvent: 09/20/2011Eventdate: REMEDY CONSTRUCTION-REMEDYCONSTRUCTEDEvent: 12/08/2010Eventdate: REMEDY CONSTRUCTION-REMEDYCONSTRUCTEDEvent: 12/08/2010Eventdate: RELEASE TO GW CONTROLLED DETERMINATION-YES, APPLICABLE AS OF THISDATEEvent: 12/08/2010Eventdate: APPROPRIATE TECHNOLOGIES II (Continued) 1000367959 TC5146125.2s Page 149 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 11/29/1995Enforcementactiondate: WRITTEN INFORMALEnforcementaction: StateViolationleadagency: 12/28/1995Dateachievedcompliance: 11/29/1995Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 270Regulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 11/29/1995Enforcementactiondate: WRITTEN INFORMALEnforcementaction: StateViolationleadagency: 12/28/1995Dateachievedcompliance: 11/29/1995Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 264.190-201.JRegulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 11/29/1995Enforcementactiondate: WRITTEN INFORMALEnforcementaction: StateViolationleadagency: 12/28/1995Dateachievedcompliance: 11/29/1995Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 264.170-177.IRegulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 11/29/1995Enforcementactiondate: WRITTEN INFORMALEnforcementaction: StateViolationleadagency: 12/28/1995Dateachievedcompliance: 11/29/1995Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 264.30-37.CRegulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: EPAEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 07/26/1996Enforcementactiondate: APPROPRIATE TECHNOLOGIES II (Continued)1000367959 TC5146125.2s Page 150 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation Not reportedEnf. disposition status: 06/02/1994Enforcementactiondate: WRITTEN INFORMALEnforcementaction: EPAViolationleadagency: 04/20/1994Dateachievedcompliance: 04/07/1994Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 264.190-201.JRegulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: Not reportedEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: Not reportedEnforcementactiondate: Not reportedEnforcementaction: StateViolationleadagency: 07/12/1994Dateachievedcompliance: 04/20/1994Dateviolationdetermined: Generators - GeneralAreaofviolation: FR - 262.10-12.ARegulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: Not reportedEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: Not reportedEnforcementactiondate: Not reportedEnforcementaction: EPAViolationleadagency: 12/07/1994Dateachievedcompliance: 07/12/1994Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 264.170-177.IRegulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: EPAEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 11/28/1994Enforcementactiondate: WRITTEN INFORMALEnforcementaction: EPAViolationleadagency: 12/07/1994Dateachievedcompliance: 11/28/1994Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 264.170-177.IRegulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: APPROPRIATE TECHNOLOGIES II (Continued)1000367959 TC5146125.2s Page 151 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 03/19/1994Enforcementactiondate: INITIAL 3008(A) COMPLIANCEEnforcementaction: StateViolationleadagency: 08/03/1995Dateachievedcompliance: 01/18/1994Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 264.190-201.JRegulationviolated: 10000Paidpenaltyamount: 10000Finalpenaltyamount: Not reportedProposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 04/19/1994Enforcementactiondate: FINAL 3008(A) COMPLIANCE ORDEREnforcementaction: StateViolationleadagency: 08/03/1995Dateachievedcompliance: 01/18/1994Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 264.50-56.DRegulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: EPAEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 06/02/1994Enforcementactiondate: WRITTEN INFORMALEnforcementaction: EPAViolationleadagency: 04/20/1994Dateachievedcompliance: 04/07/1994Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 270Regulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: Not reportedEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: Not reportedEnforcementactiondate: Not reportedEnforcementaction: EPAViolationleadagency: 04/20/1994Dateachievedcompliance: 04/07/1994Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 264.190-201.JRegulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: EPAEnforcementleadagency: Not reportedEnf. disp. status date: APPROPRIATE TECHNOLOGIES II (Continued)1000367959 TC5146125.2s Page 152 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 03/19/1994Enforcementactiondate: INITIAL 3008(A) COMPLIANCEEnforcementaction: StateViolationleadagency: 08/03/1995Dateachievedcompliance: 01/18/1994Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 264.50-56.DRegulationviolated: 10000Paidpenaltyamount: 10000Finalpenaltyamount: Not reportedProposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 04/19/1994Enforcementactiondate: FINAL 3008(A) COMPLIANCE ORDEREnforcementaction: StateViolationleadagency: 08/03/1995Dateachievedcompliance: 01/18/1994Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 264.170-177.IRegulationviolated: 10000Paidpenaltyamount: 10000Finalpenaltyamount: Not reportedProposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 04/19/1994Enforcementactiondate: FINAL 3008(A) COMPLIANCE ORDEREnforcementaction: StateViolationleadagency: 08/03/1995Dateachievedcompliance: 01/18/1994Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 264.190-201.JRegulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: 37000Proposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 03/19/1994Enforcementactiondate: INITIAL 3008(A) COMPLIANCEEnforcementaction: StateViolationleadagency: 08/03/1995Dateachievedcompliance: 01/18/1994Dateviolationdetermined: TSD - Closure/Post-ClosureAreaofviolation: FR - 264.110-120.GRegulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: 37000Proposedpenaltyamount: StateEnforcementleadagency: APPROPRIATE TECHNOLOGIES II (Continued)1000367959 TC5146125.2s Page 153 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation Not reportedProposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 01/18/1994Enforcementactiondate: WRITTEN INFORMALEnforcementaction: StateViolationleadagency: 08/03/1995Dateachievedcompliance: 01/18/1994Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 270Regulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: 37000Proposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 03/19/1994Enforcementactiondate: INITIAL 3008(A) COMPLIANCEEnforcementaction: StateViolationleadagency: 08/03/1995Dateachievedcompliance: 01/18/1994Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 270Regulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 01/18/1994Enforcementactiondate: WRITTEN INFORMALEnforcementaction: StateViolationleadagency: 08/03/1995Dateachievedcompliance: 01/18/1994Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 264.190-201.JRegulationviolated: 10000Paidpenaltyamount: 10000Finalpenaltyamount: Not reportedProposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 04/19/1994Enforcementactiondate: FINAL 3008(A) COMPLIANCE ORDEREnforcementaction: StateViolationleadagency: 08/03/1995Dateachievedcompliance: 01/18/1994Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 270Regulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: 37000Proposedpenaltyamount: APPROPRIATE TECHNOLOGIES II (Continued)1000367959 TC5146125.2s Page 154 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 01/18/1994Enforcementactiondate: WRITTEN INFORMALEnforcementaction: StateViolationleadagency: 08/03/1995Dateachievedcompliance: 01/18/1994Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 264.50-56.DRegulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 01/18/1994Enforcementactiondate: WRITTEN INFORMALEnforcementaction: StateViolationleadagency: 08/03/1995Dateachievedcompliance: 01/18/1994Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 264.170-177.IRegulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: 37000Proposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 03/19/1994Enforcementactiondate: INITIAL 3008(A) COMPLIANCEEnforcementaction: StateViolationleadagency: 08/03/1995Dateachievedcompliance: 01/18/1994Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 264.170-177.IRegulationviolated: 10000Paidpenaltyamount: 10000Finalpenaltyamount: Not reportedProposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 04/19/1994Enforcementactiondate: FINAL 3008(A) COMPLIANCE ORDEREnforcementaction: StateViolationleadagency: 08/03/1995Dateachievedcompliance: 01/18/1994Dateviolationdetermined: TSD - Closure/Post-ClosureAreaofviolation: FR - 264.110-120.GRegulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: APPROPRIATE TECHNOLOGIES II (Continued)1000367959 TC5146125.2s Page 155 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: Not reportedEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: Not reportedEnforcementactiondate: Not reportedEnforcementaction: EPAViolationleadagency: 12/14/1993Dateachievedcompliance: 03/10/1992Dateviolationdetermined: TSD - FinancialRequirementsAreaofviolation: F - 264.140-150.HRegulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: Not reportedEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: Not reportedEnforcementactiondate: Not reportedEnforcementaction: StateViolationleadagency: 01/21/1993Dateachievedcompliance: 07/08/1992Dateviolationdetermined: Generators - GeneralAreaofviolation: FR - 262.10-12.ARegulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 01/18/1994Enforcementactiondate: WRITTEN INFORMALEnforcementaction: StateViolationleadagency: 12/14/1993Dateachievedcompliance: 06/22/1993Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 264.170-177.IRegulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 01/18/1994Enforcementactiondate: WRITTEN INFORMALEnforcementaction: StateViolationleadagency: 08/03/1995Dateachievedcompliance: 01/18/1994Dateviolationdetermined: TSD - Closure/Post-ClosureAreaofviolation: FR - 264.110-120.GRegulationviolated: Not reportedPaidpenaltyamount: APPROPRIATE TECHNOLOGIES II (Continued)1000367959 TC5146125.2s Page 156 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation FR - 270Regulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 05/30/1991Enforcementactiondate: INITIAL 3008(A) COMPLIANCEEnforcementaction: StateViolationleadagency: 05/30/1991Dateachievedcompliance: 10/16/1990Dateviolationdetermined: LDR - GeneralAreaofviolation: FR - 268.7Regulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 05/30/1991Enforcementactiondate: INITIAL 3008(A) COMPLIANCEEnforcementaction: StateViolationleadagency: 05/30/1991Dateachievedcompliance: 10/16/1990Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 270Regulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 05/30/1991Enforcementactiondate: INITIAL 3008(A) COMPLIANCEEnforcementaction: StateViolationleadagency: 05/30/1991Dateachievedcompliance: 10/16/1990Dateviolationdetermined: LDR - GeneralAreaofviolation: FR - 268ALLRegulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: Not reportedEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: Not reportedEnforcementactiondate: Not reportedEnforcementaction: EPAViolationleadagency: 12/14/1993Dateachievedcompliance: 11/22/1991Dateviolationdetermined: TSD - FinancialRequirementsAreaofviolation: F - 264.140-150.HRegulationviolated: APPROPRIATE TECHNOLOGIES II (Continued)1000367959 TC5146125.2s Page 157 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation LDR - GeneralAreaofviolation: FR - 268ALLRegulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 06/07/1990Enforcementactiondate: WRITTEN INFORMALEnforcementaction: StateViolationleadagency: 08/27/1990Dateachievedcompliance: 04/26/1990Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 270Regulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: EPAEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 01/23/1991Enforcementactiondate: WRITTEN INFORMALEnforcementaction: EPAViolationleadagency: 10/16/1990Dateachievedcompliance: 09/25/1990Dateviolationdetermined: LDR - GeneralAreaofviolation: FR - 268.7Regulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: EPAEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 01/23/1991Enforcementactiondate: WRITTEN INFORMALEnforcementaction: EPAViolationleadagency: 10/16/1990Dateachievedcompliance: 09/25/1990Dateviolationdetermined: LDR - GeneralAreaofviolation: FR - 268ALLRegulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 11/29/1990Enforcementactiondate: WRITTEN INFORMALEnforcementaction: StateViolationleadagency: 05/30/1991Dateachievedcompliance: 10/16/1990Dateviolationdetermined: TSD - GeneralAreaofviolation: APPROPRIATE TECHNOLOGIES II (Continued)1000367959 TC5146125.2s Page 158 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 03/20/1989Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 270Regulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: EPAEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 03/08/1990Enforcementactiondate: WRITTEN INFORMALEnforcementaction: EPAViolationleadagency: 09/07/1990Dateachievedcompliance: 12/06/1989Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 270Regulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: EPAEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 03/08/1990Enforcementactiondate: WRITTEN INFORMALEnforcementaction: EPAViolationleadagency: 09/07/1990Dateachievedcompliance: 12/06/1989Dateviolationdetermined: LDR - GeneralAreaofviolation: FR - 268.7Regulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: EPAEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 03/08/1990Enforcementactiondate: WRITTEN INFORMALEnforcementaction: EPAViolationleadagency: 09/07/1990Dateachievedcompliance: 12/06/1989Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 264.70-77.ERegulationviolated: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: EPAEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 03/08/1990Enforcementactiondate: WRITTEN INFORMALEnforcementaction: EPAViolationleadagency: 09/07/1990Dateachievedcompliance: 12/06/1989Dateviolationdetermined: APPROPRIATE TECHNOLOGIES II (Continued)1000367959 TC5146125.2s Page 159 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 12/08/1997Evaluationdate: Evaluation Action Summary: Not reportedPaidpenaltyamount: Not reportedFinalpenaltyamount: Not reportedProposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 06/13/1988Enforcementactiondate: WRITTEN INFORMALEnforcementaction: StateViolationleadagency: 08/12/1988Dateachievedcompliance: 06/01/1988Dateviolationdetermined: TSD - GeneralAreaofviolation: FR - 270Regulationviolated: Not reportedPaidpenaltyamount: 24000Finalpenaltyamount: 24000Proposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 07/10/1989Enforcementactiondate: INITIAL 3008(A) COMPLIANCEEnforcementaction: StateViolationleadagency: 08/23/1989Dateachievedcompliance: 03/20/1989Dateviolationdetermined: LDR - GeneralAreaofviolation: FR - 268ALLRegulationviolated: Not reportedPaidpenaltyamount: 24000Finalpenaltyamount: 24000Proposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 07/10/1989Enforcementactiondate: INITIAL 3008(A) COMPLIANCEEnforcementaction: StateViolationleadagency: 08/23/1989Dateachievedcompliance: 03/20/1989Dateviolationdetermined: LDR - GeneralAreaofviolation: FR - 268.7Regulationviolated: Not reportedPaidpenaltyamount: 24000Finalpenaltyamount: 24000Proposedpenaltyamount: StateEnforcementleadagency: Not reportedEnf. disp. status date: Not reportedEnf. disposition status: 07/10/1989Enforcementactiondate: INITIAL 3008(A) COMPLIANCEEnforcementaction: StateViolationleadagency: 08/23/1989Dateachievedcompliance: APPROPRIATE TECHNOLOGIES II (Continued)1000367959 TC5146125.2s Page 160 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation EPAEvaluationleadagency: 12/07/1994Dateachievedcompliance: TSD - GeneralAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 07/12/1994Evaluationdate: StateEvaluationleadagency: NotreportedDateachievedcompliance: NotreportedAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 11/29/1994Evaluationdate: EPAEvaluationleadagency: 11/29/1995Dateachievedcompliance: TSD - GeneralAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 05/25/1995Evaluationdate: StateEvaluationleadagency: NotreportedDateachievedcompliance: NotreportedAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 11/29/1995Evaluationdate: StateEvaluationleadagency: 12/28/1995Dateachievedcompliance: TSD - GeneralAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 11/29/1995Evaluationdate: StateEvaluationleadagency: NotreportedDateachievedcompliance: NotreportedAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 05/08/1996Evaluationdate: EPAEvaluationleadagency: NotreportedDateachievedcompliance: NotreportedAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 06/11/1996Evaluationdate: EPAEvaluationleadagency: NotreportedDateachievedcompliance: NotreportedAreaofviolation: NON-FINANCIAL RECORDREVIEWEvaluation: 10/25/1996Evaluationdate: StateEvaluationleadagency: NotreportedDateachievedcompliance: NotreportedAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 11/26/1996Evaluationdate: StateEvaluationleadagency: NotreportedDateachievedcompliance: APPROPRIATE TECHNOLOGIES II (Continued) 1000367959 TC5146125.2s Page 161 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation NotreportedAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 04/16/1992Evaluationdate: State Contractor/GranteeEvaluationleadagency: 01/21/1993Dateachievedcompliance: Generators - GeneralAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 07/08/1992Evaluationdate: EPA-Initiated Oversight/Observation/TrainingActionsEvaluationleadagency: NotreportedDateachievedcompliance: NotreportedAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 01/21/1993Evaluationdate: StateEvaluationleadagency: NotreportedDateachievedcompliance: NotreportedAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 01/21/1993Evaluationdate: StateEvaluationleadagency: 12/14/1993Dateachievedcompliance: TSD - GeneralAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 06/21/1993Evaluationdate: StateEvaluationleadagency: 08/03/1995Dateachievedcompliance: TSD - Closure/Post-ClosureAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 12/06/1993Evaluationdate: StateEvaluationleadagency: 08/03/1995Dateachievedcompliance: TSD - GeneralAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 12/06/1993Evaluationdate: EPAEvaluationleadagency: 04/20/1994Dateachievedcompliance: TSD - GeneralAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 03/03/1994Evaluationdate: State Contractor/GranteeEvaluationleadagency: 07/12/1994Dateachievedcompliance: Generators - GeneralAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 04/20/1994Evaluationdate: EPA Contractor/GranteeEvaluationleadagency: 12/07/1994Dateachievedcompliance: TSD - GeneralAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 07/12/1994Evaluationdate: APPROPRIATE TECHNOLOGIES II (Continued) 1000367959 TC5146125.2s Page 162 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation StateEvaluationleadagency: NotreportedDateachievedcompliance: NotreportedAreaofviolation: FINANCIAL RECORDREVIEWEvaluation: 05/08/1990Evaluationdate: EPAEvaluationleadagency: 10/16/1990Dateachievedcompliance: LDR - GeneralAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 09/25/1990Evaluationdate: StateEvaluationleadagency: NotreportedDateachievedcompliance: NotreportedAreaofviolation: FINANCIAL RECORDREVIEWEvaluation: 10/02/1990Evaluationdate: StateEvaluationleadagency: 05/30/1991Dateachievedcompliance: LDR - GeneralAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 10/16/1990Evaluationdate: StateEvaluationleadagency: 05/30/1991Dateachievedcompliance: TSD - GeneralAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 10/16/1990Evaluationdate: EPAEvaluationleadagency: NotreportedDateachievedcompliance: NotreportedAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 04/18/1991Evaluationdate: StateEvaluationleadagency: NotreportedDateachievedcompliance: NotreportedAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 10/22/1991Evaluationdate: EPA Contractor/GranteeEvaluationleadagency: 12/14/1993Dateachievedcompliance: TSD - FinancialRequirementsAreaofviolation: FINANCIAL RECORDREVIEWEvaluation: 11/22/1991Evaluationdate: EPA Contractor/GranteeEvaluationleadagency: 12/14/1993Dateachievedcompliance: TSD - FinancialRequirementsAreaofviolation: FINANCIAL RECORDREVIEWEvaluation: 03/10/1992Evaluationdate: StateEvaluationleadagency: NotreportedDateachievedcompliance: APPROPRIATE TECHNOLOGIES II (Continued) 1000367959 TC5146125.2s Page 163 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation CALocationState: CHULAVISTALocationCity: NotreportedTotalTanks: NotreportedLocationAddress2: BPCode: 1700 MAXWELLROADLocationAddress1: NotreportedFacilityStatus: CAT080010101EPAID: USACountry: NY MANIFEST: NotreportedAction: 9Region: CAT080010101EPAID: 2020 COR ACTION: StateEvaluationleadagency: 08/12/1988Dateachievedcompliance: TSD - GeneralAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 06/01/1988Evaluationdate: StateEvaluationleadagency: NotreportedDateachievedcompliance: NotreportedAreaofviolation: FINANCIAL RECORDREVIEWEvaluation: 06/06/1988Evaluationdate: StateEvaluationleadagency: 08/23/1989Dateachievedcompliance: LDR - GeneralAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 03/20/1989Evaluationdate: StateEvaluationleadagency: 08/23/1989Dateachievedcompliance: TSD - GeneralAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 03/20/1989Evaluationdate: EPAEvaluationleadagency: 09/07/1990Dateachievedcompliance: LDR - GeneralAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 12/06/1989Evaluationdate: EPAEvaluationleadagency: 09/07/1990Dateachievedcompliance: TSD - GeneralAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 12/06/1989Evaluationdate: StateEvaluationleadagency: 08/27/1990Dateachievedcompliance: TSD - GeneralAreaofviolation: COMPLIANCE EVALUATION INSPECTION ON-SITEEvaluation: 04/26/1990Evaluationdate: APPROPRIATE TECHNOLOGIES II (Continued) 1000367959 TC5146125.2s Page 164 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation B Incineration, heat recovery, burning.Handling Method: DF - Fiberboard or plastic drums (glass)Container Type: 001NumberofContainers: P - PoundsUnits: 00008Quantity: NotreportedWasteCode: NotreportedWasteCode: NotreportedWasteCode: NotreportedWasteCode: NotreportedWasteCode: D001 - NON-LISTED IGNITABLEWASTESWasteCode: NotreportedMGMTMethodTypeCode: NotreportedAltFacilitySignDate: NotreportedAltFacilityRCRAID: NotreportedManifestRefNumber: NotreportedDiscrFullRejectIndicator: NotreportedDiscrPartialRejectIndicator: NotreportedDiscrResidueIndicator: NotreportedDiscrTypeIndicator: NotreportedDiscrQuantityIndicator: NotreportedExportIndicator: NotreportedImportIndicator: NotreportedManifestTrackingNumber: NotreportedTSDFID2: NYD000632372TSDFID1: NotreportedTrans2EPAID: NYD980769947Trans1EPAID: CAT080010101GeneratorEPAID: 10/22/1996PartBRecvDate: Part A Recv Date: 10/04/1996TSDSiteRecvDate: Trans2 Recv Date: 09/16/1996Trans1RecvDate: 09/16/1996GeneratorShipDate: NotreportedTrans2StateID: 11284PNYTrans1StateID: 1996Year: Notreportedseq: KManifestStatus: NYB7314453DocumentID: NY MANIFEST: 6194211175MailingPhone: USAMailingCountry: NotreportedMailingZip4: 92011MailingZip: CAMailingState: CHULAVISTAMailingCity: NotreportedMailingAddress2: 1700 MAXWELLROADMailingAddress1: APPROPRIATE TECHNOLOGIESIIMailingContact: APPROPRIATE TECHNOLOGIESIIMailingName: CAT080010101EPAID: NY MANIFEST: NotreportedLocationZip4: 92011LocationZip: APPROPRIATE TECHNOLOGIES II (Continued)1000367959 TC5146125.2s Page 165 MAPFINDINGSMapID Direction EDR IDNumberDistance EPA IDNumberDatabase(s)SiteElevation 35 additional NY_MANIFEST: record(s) in the EDR Site Report. Click this hyperlink while viewing on your computer to access 100SpecificGravity: T Chemical, physical, or biological treatment.Handling Method: DF - Fiberboard or plastic drums (glass)Container Type: 001NumberofContainers: P - PoundsUnits: 00234Quantity: P098 - POTASSIUMCYANIDEWasteCode: 100SpecificGravity: T Chemical, physical, or biological treatment.Handling Method: DF - Fiberboard or plastic drums (glass)Container Type: 001NumberofContainers: P - PoundsUnits: 00234Quantity: P098 - POTASSIUMCYANIDEWasteCode: 100SpecificGravity: B Incineration, heat recovery, burning.Handling Method: DF - Fiberboard or plastic drums (glass)Container Type: 001NumberofContainers: P - PoundsUnits: 00008Quantity: NotreportedWasteCode: NotreportedWasteCode: NotreportedWasteCode: NotreportedWasteCode: D001 - NON-LISTED IGNITABLEWASTESWasteCode: 100SpecificGravity: T Chemical, physical, or biological treatment.Handling Method: DF - Fiberboard or plastic drums (glass)Container Type: 001NumberofContainers: P - PoundsUnits: 00126Quantity: NotreportedWasteCode: NotreportedWasteCode: NotreportedWasteCode: NotreportedWasteCode: D001 - NON-LISTED IGNITABLEWASTESWasteCode: 100SpecificGravity: T Chemical, physical, or biological treatment.Handling Method: DF - Fiberboard or plastic drums (glass)Container Type: 001NumberofContainers: P - PoundsUnits: 00011Quantity: NotreportedWasteCode: NotreportedWasteCode: NotreportedWasteCode: NotreportedWasteCode: D001 - NON-LISTED IGNITABLEWASTESWasteCode: 100SpecificGravity: APPROPRIATE TECHNOLOGIES II (Continued) 1000367959 TC5146125.2s Page 166 To maintain currency of the following federal and state databases, EDR contacts the appropriate governmental agency on a monthly or quarterly basis, as required. Number of Days to Update:Provides confirmation that EDR is reporting records that have been updated within 90 days from the date the government agency made the information available to the public. STANDARD ENVIRONMENTAL RECORDS Federal NPL site list NPL: National Priority List National Priorities List (Superfund). The NPL is a subset of CERCLIS and identifies over 1,200 sites for priority cleanup under the Superfund Program. NPL sites may encompass relatively large areas. As such, EDR provides polygon coverage for over 1,000 NPL site boundaries produced by EPA’s Environmental Photographic Interpretation Center EPIC) and regional EPA offices. Date of Government Version: 10/10/2017 Date Data Arrived at EDR: 11/03/2017 Date Made Active in Reports: 12/15/2017 Number of Days to Update: 42 Source: EPA Telephone: N/A Last EDR Contact: 12/22/2017 Next Scheduled EDR Contact: 01/15/2018 Data Release Frequency: Quarterly NPL Site Boundaries Sources: EPA’s Environmental Photographic Interpretation Center (EPIC) Telephone: 202-564-7333 EPA Region 1 EPA Region 6 Telephone 617-918-1143 Telephone: 214-655-6659 EPA Region 3 EPA Region 7 Telephone 215-814-5418 Telephone: 913-551-7247 EPA Region 4 EPA Region 8 Telephone 404-562-8033 Telephone: 303-312-6774 EPA Region 5 EPA Region 9 Telephone 312-886-6686 Telephone: 415-947-4246 EPA Region 10 Telephone 206-553-8665 Proposed NPL: Proposed National Priority List Sites A site that has been proposed for listing on the National Priorities List through the issuance of a proposed rule in the Federal Register. EPA then accepts public comments on the site, responds to the comments, and places on the NPL those sites that continue to meet the requirements for listing. Date of Government Version: 10/10/2017 Date Data Arrived at EDR: 11/03/2017 Date Made Active in Reports: 12/15/2017 Number of Days to Update: 42 Source: EPA Telephone: N/A Last EDR Contact: 12/22/2017 Next Scheduled EDR Contact: 01/15/2018 Data Release Frequency: Quarterly NPL LIENS: Federal Superfund Liens Federal Superfund Liens. Under the authority granted the USEPA by CERCLA of 1980, the USEPA has the authority to file liens against real property in order to recover remedial action expenditures or when the property owner received notification of potential liability. USEPA compiles a listing of filed notices of Superfund Liens. Date of Government Version: 10/15/1991 Date Data Arrived at EDR: 02/02/1994 Date Made Active in Reports: 03/30/1994 Number of Days to Update: 56 Source: EPA Telephone: 202-564-4267 Last EDR Contact: 08/15/2011 Next Scheduled EDR Contact: 11/28/2011 Data Release Frequency: No Update Planned TC5146125.2s Page GR-1 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Federal Delisted NPL site list Delisted NPL: National Priority List Deletions The National Oil and Hazardous Substances Pollution Contingency Plan (NCP) establishes the criteria that the EPA uses to delete sites from the NPL. In accordance with 40 CFR 300.425.(e), sites may be deleted from the NPL where no further response is appropriate. Date of Government Version: 10/10/2017 Date Data Arrived at EDR: 11/03/2017 Date Made Active in Reports: 12/15/2017 Number of Days to Update: 42 Source: EPA Telephone: N/A Last EDR Contact: 12/22/2017 Next Scheduled EDR Contact: 01/15/2018 Data Release Frequency: Quarterly Federal CERCLIS list FEDERAL FACILITY: Federal Facility Site Information listing A listing of National Priority List (NPL) and Base Realignment and Closure (BRAC) sites found in the Comprehensive Environmental Response, Compensation and Liability Information System (CERCLIS) Database where EPA Federal Facilities Restoration and Reuse Office is involved in cleanup activities. Date of Government Version: 11/07/2016 Date Data Arrived at EDR: 01/05/2017 Date Made Active in Reports: 04/07/2017 Number of Days to Update: 92 Source: Environmental Protection Agency Telephone: 703-603-8704 Last EDR Contact: 10/06/2017 Next Scheduled EDR Contact: 01/15/2018 Data Release Frequency: Varies SEMS: Superfund Enterprise Management System SEMS (Superfund Enterprise Management System) tracks hazardous waste sites, potentially hazardous waste sites, and remedial activities performed in support of EPA’s Superfund Program across the United States. The list was formerly know as CERCLIS, renamed to SEMS by the EPA in 2015. The list contains data on potentially hazardous waste sites that have been reported to the USEPA by states, municipalities, private companies and private persons, pursuant to Section 103 of the Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA). This dataset also contains sites which are either proposed to or on the National Priorities List (NPL) and the sites which are in the screening and assessment phase for possible inclusion on the NPL. Date of Government Version: 07/11/2017 Date Data Arrived at EDR: 07/21/2017 Date Made Active in Reports: 10/06/2017 Number of Days to Update: 77 Source: EPA Telephone: 800-424-9346 Last EDR Contact: 12/22/2017 Next Scheduled EDR Contact: 01/29/2018 Data Release Frequency: Quarterly Federal CERCLIS NFRAP site list SEMS-ARCHIVE: Superfund Enterprise Management System Archive TC5146125.2s Page GR-2 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING SEMS-ARCHIVE (Superfund Enterprise Management System Archive) tracks sites that have no further interest under the Federal Superfund Program based on available information. The list was formerly known as the CERCLIS-NFRAP, renamed to SEMS ARCHIVE by the EPA in 2015. EPA may perform a minimal level of assessment work at a site while it is archived if site conditions change and/or new information becomes available. Archived sites have been removed and archived from the inventory of SEMS sites. Archived status indicates that, to the best of EPA’s knowledge, assessment at a site has been completed and that EPA has determined no further steps will be taken to list the site on the National Priorities List (NPL), unless information indicates this decision was not appropriate or other considerations require a recommendation for listing at a later time. The decision does not necessarily mean that there is no hazard associated with a given site; it only means that. based upon available information, the location is not judged to be potential NPL site. Date of Government Version: 07/11/2017 Date Data Arrived at EDR: 07/28/2017 Date Made Active in Reports: 10/06/2017 Number of Days to Update: 70 Source: EPA Telephone: 800-424-9346 Last EDR Contact: 12/22/2017 Next Scheduled EDR Contact: 01/29/2018 Data Release Frequency: Quarterly Federal RCRA CORRACTS facilities list CORRACTS: Corrective Action Report CORRACTS identifies hazardous waste handlers with RCRA corrective action activity. Date of Government Version: 09/13/2017 Date Data Arrived at EDR: 09/26/2017 Date Made Active in Reports: 10/06/2017 Number of Days to Update: 10 Source: EPA Telephone: 800-424-9346 Last EDR Contact: 09/26/2017 Next Scheduled EDR Contact: 01/08/2018 Data Release Frequency: Quarterly Federal RCRA non-CORRACTS TSD facilities list RCRA-TSDF: RCRA - Treatment, Storage and Disposal RCRAInfo is EPA’s comprehensive information system, providing access to data supporting the Resource Conservation and Recovery Act (RCRA) of 1976 and the Hazardous and Solid Waste Amendments (HSWA) of 1984. The database includes selective information on sites which generate, transport, store, treat and/or dispose of hazardous waste as defined by the Resource Conservation and Recovery Act (RCRA). Transporters are individuals or entities that move hazardous waste from the generator offsite to a facility that can recycle, treat, store, or dispose of the waste. TSDFs treat, store, or dispose of the waste. Date of Government Version: 09/13/2017 Date Data Arrived at EDR: 09/26/2017 Date Made Active in Reports: 10/06/2017 Number of Days to Update: 10 Source: Environmental Protection Agency Telephone: (415) 495-8895 Last EDR Contact: 09/26/2017 Next Scheduled EDR Contact: 01/08/2018 Data Release Frequency: Quarterly Federal RCRA generators list RCRA-LQG: RCRA - Large Quantity Generators RCRAInfo is EPA’s comprehensive information system, providing access to data supporting the Resource Conservation and Recovery Act (RCRA) of 1976 and the Hazardous and Solid Waste Amendments (HSWA) of 1984. The database includes selective information on sites which generate, transport, store, treat and/or dispose of hazardous waste as defined by the Resource Conservation and Recovery Act (RCRA). Large quantity generators (LQGs) generate over 1,000 kilograms (kg) of hazardous waste, or over 1 kg of acutely hazardous waste per month. Date of Government Version: 09/13/2017 Date Data Arrived at EDR: 09/26/2017 Date Made Active in Reports: 10/06/2017 Number of Days to Update: 10 Source: Environmental Protection Agency Telephone: (415) 495-8895 Last EDR Contact: 09/26/2017 Next Scheduled EDR Contact: 01/08/2018 Data Release Frequency: Quarterly TC5146125.2s Page GR-3 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING RCRA-SQG: RCRA - Small Quantity Generators RCRAInfo is EPA’s comprehensive information system, providing access to data supporting the Resource Conservation and Recovery Act (RCRA) of 1976 and the Hazardous and Solid Waste Amendments (HSWA) of 1984. The database includes selective information on sites which generate, transport, store, treat and/or dispose of hazardous waste as defined by the Resource Conservation and Recovery Act (RCRA). Small quantity generators (SQGs) generate between 100 kg and 1,000 kg of hazardous waste per month. Date of Government Version: 09/13/2017 Date Data Arrived at EDR: 09/26/2017 Date Made Active in Reports: 10/06/2017 Number of Days to Update: 10 Source: Environmental Protection Agency Telephone: (415) 495-8895 Last EDR Contact: 09/26/2017 Next Scheduled EDR Contact: 01/08/2018 Data Release Frequency: Quarterly RCRA-CESQG: RCRA - Conditionally Exempt Small Quantity Generators RCRAInfo is EPA’s comprehensive information system, providing access to data supporting the Resource Conservation and Recovery Act (RCRA) of 1976 and the Hazardous and Solid Waste Amendments (HSWA) of 1984. The database includes selective information on sites which generate, transport, store, treat and/or dispose of hazardous waste as defined by the Resource Conservation and Recovery Act (RCRA). Conditionally exempt small quantity generators CESQGs) generate less than 100 kg of hazardous waste, or less than 1 kg of acutely hazardous waste per month. Date of Government Version: 09/13/2017 Date Data Arrived at EDR: 09/26/2017 Date Made Active in Reports: 10/06/2017 Number of Days to Update: 10 Source: Environmental Protection Agency Telephone: (415) 495-8895 Last EDR Contact: 09/26/2017 Next Scheduled EDR Contact: 01/08/2018 Data Release Frequency: Quarterly Federal institutional controls / engineering controls registries LUCIS: Land Use Control Information System LUCIS contains records of land use control information pertaining to the former Navy Base Realignment and Closure properties. Date of Government Version: 05/22/2017 Date Data Arrived at EDR: 06/13/2017 Date Made Active in Reports: 09/15/2017 Number of Days to Update: 94 Source: Department of the Navy Telephone: 843-820-7326 Last EDR Contact: 11/08/2017 Next Scheduled EDR Contact: 02/26/2018 Data Release Frequency: Varies US ENG CONTROLS: Engineering Controls Sites List A listing of sites with engineering controls in place. Engineering controls include various forms of caps, building foundations, liners, and treatment methods to create pathway elimination for regulated substances to enter environmental media or effect human health. Date of Government Version: 08/10/2017 Date Data Arrived at EDR: 08/30/2017 Date Made Active in Reports: 10/13/2017 Number of Days to Update: 44 Source: Environmental Protection Agency Telephone: 703-603-0695 Last EDR Contact: 11/27/2017 Next Scheduled EDR Contact: 03/12/2018 Data Release Frequency: Varies US INST CONTROL: Sites with Institutional Controls A listing of sites with institutional controls in place. Institutional controls include administrative measures, such as groundwater use restrictions, construction restrictions, property use restrictions, and post remediation care requirements intended to prevent exposure to contaminants remaining on site. Deed restrictions are generally required as part of the institutional controls. Date of Government Version: 08/10/2017 Date Data Arrived at EDR: 08/30/2017 Date Made Active in Reports: 10/13/2017 Number of Days to Update: 44 Source: Environmental Protection Agency Telephone: 703-603-0695 Last EDR Contact: 11/27/2017 Next Scheduled EDR Contact: 03/12/2018 Data Release Frequency: Varies TC5146125.2s Page GR-4 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Federal ERNS list ERNS: Emergency Response Notification System Emergency Response Notification System. ERNS records and stores information on reported releases of oil and hazardous substances. Date of Government Version: 09/18/2017 Date Data Arrived at EDR: 09/21/2017 Date Made Active in Reports: 10/13/2017 Number of Days to Update: 22 Source: National Response Center, United States Coast Guard Telephone: 202-267-2180 Last EDR Contact: 09/21/2017 Next Scheduled EDR Contact: 01/08/2018 Data Release Frequency: Quarterly State- and tribal - equivalent NPL RESPONSE: State Response Sites Identifies confirmed release sites where DTSC is involved in remediation, either in a lead or oversight capacity. These confirmed release sites are generally high-priority and high potential risk. Date of Government Version: 10/30/2017 Date Data Arrived at EDR: 10/31/2017 Date Made Active in Reports: 12/15/2017 Number of Days to Update: 45 Source: Department of Toxic Substances Control Telephone: 916-323-3400 Last EDR Contact: 10/31/2017 Next Scheduled EDR Contact: 02/12/2018 Data Release Frequency: Quarterly State- and tribal - equivalent CERCLIS ENVIROSTOR: EnviroStor Database The Department of Toxic Substances Control’s (DTSC’s) Site Mitigation and Brownfields Reuse Program’s (SMBRP’s) EnviroStor database identifes sites that have known contamination or sites for which there may be reasons to investigate further. The database includes the following site types: Federal Superfund sites (National Priorities List (NPL)); State Response, including Military Facilities and State Superfund; Voluntary Cleanup; and School sites. EnviroStor provides similar information to the information that was available in CalSites, and provides additional site information, including, but not limited to, identification of formerly-contaminated properties that have been released for reuse, properties where environmental deed restrictions have been recorded to prevent inappropriate land uses, and risk characterization information that is used to assess potential impacts to public health and the environment at contaminated sites. Date of Government Version: 10/30/2017 Date Data Arrived at EDR: 10/31/2017 Date Made Active in Reports: 12/15/2017 Number of Days to Update: 45 Source: Department of Toxic Substances Control Telephone: 916-323-3400 Last EDR Contact: 10/31/2017 Next Scheduled EDR Contact: 02/12/2018 Data Release Frequency: Quarterly State and tribal landfill and/or solid waste disposal site lists SWF/LF (SWIS): Solid Waste Information System Active, Closed and Inactive Landfills. SWF/LF records typically contain an inve ntory of solid waste disposal facilities or landfills. These may be active or i nactive facilities or open dumps that failed to meet RCRA Section 4004 criteria for solid waste landfills or disposal sites. Date of Government Version: 11/13/2017 Date Data Arrived at EDR: 11/14/2017 Date Made Active in Reports: 12/07/2017 Number of Days to Update: 23 Source: Department of Resources Recycling and Recovery Telephone: 916-341-6320 Last EDR Contact: 11/14/2017 Next Scheduled EDR Contact: 02/26/2018 Data Release Frequency: Quarterly State and tribal leaking storage tank lists TC5146125.2s Page GR-5 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING LUST REG 2: Fuel Leak List Leaking Underground Storage Tank locations. Alameda, Contra Costa, Marin, Napa, San Francisco, San Mateo, Santa Clara, Solano, Sonoma counties. Date of Government Version: 09/30/2004 Date Data Arrived at EDR: 10/20/2004 Date Made Active in Reports: 11/19/2004 Number of Days to Update: 30 Source: California Regional Water Quality Control Board San Francisco Bay Region (2) Telephone: 510-622-2433 Last EDR Contact: 09/19/2011 Next Scheduled EDR Contact: 01/02/2012 Data Release Frequency: Quarterly LUST REG 9: Leaking Underground Storage Tank Report Orange, Riverside, San Diego counties. For more current information, please refer to the State Water Resources Control Board’s LUST database. Date of Government Version: 03/01/2001 Date Data Arrived at EDR: 04/23/2001 Date Made Active in Reports: 05/21/2001 Number of Days to Update: 28 Source: California Regional Water Quality Control Board San Diego Region (9) Telephone: 858-637-5595 Last EDR Contact: 09/26/2011 Next Scheduled EDR Contact: 01/09/2012 Data Release Frequency: No Update Planned LUST REG 8: Leaking Underground Storage Tanks California Regional Water Quality Control Board Santa Ana Region (8). For more current information, please refer to the State Water Resources Control Board’s LUST database. Date of Government Version: 02/14/2005 Date Data Arrived at EDR: 02/15/2005 Date Made Active in Reports: 03/28/2005 Number of Days to Update: 41 Source: California Regional Water Quality Control Board Santa Ana Region (8) Telephone: 909-782-4496 Last EDR Contact: 08/15/2011 Next Scheduled EDR Contact: 11/28/2011 Data Release Frequency: Varies LUST REG 6L: Leaking Underground Storage Tank Case Listing For more current information, please refer to the State Water Resources Control Board’s LUST database. Date of Government Version: 09/09/2003 Date Data Arrived at EDR: 09/10/2003 Date Made Active in Reports: 10/07/2003 Number of Days to Update: 27 Source: California Regional Water Quality Control Board Lahontan Region (6) Telephone: 530-542-5572 Last EDR Contact: 09/12/2011 Next Scheduled EDR Contact: 12/26/2011 Data Release Frequency: No Update Planned LUST REG 5: Leaking Underground Storage Tank Database Leaking Underground Storage Tank locations. Alameda, Alpine, Amador, Butte, Colusa, Contra Costa, Calveras, El Dorado, Fresno, Glenn, Kern, Kings, Lake, Lassen, Madera, Mariposa, Merced, Modoc, Napa, Nevada, Placer, Plumas, Sacramento, San Joaquin, Shasta, Solano, Stanislaus, Sutter, Tehama, Tulare, Tuolumne, Yolo, Yuba counties. Date of Government Version: 07/01/2008 Date Data Arrived at EDR: 07/22/2008 Date Made Active in Reports: 07/31/2008 Number of Days to Update: 9 Source: California Regional Water Quality Control Board Central Valley Region (5) Telephone: 916-464-4834 Last EDR Contact: 07/01/2011 Next Scheduled EDR Contact: 10/17/2011 Data Release Frequency: No Update Planned LUST REG 4: Underground Storage Tank Leak List Los Angeles, Ventura counties. For more current information, please refer to the State Water Resources Control Board’s LUST database. Date of Government Version: 09/07/2004 Date Data Arrived at EDR: 09/07/2004 Date Made Active in Reports: 10/12/2004 Number of Days to Update: 35 Source: California Regional Water Quality Control Board Los Angeles Region (4) Telephone: 213-576-6710 Last EDR Contact: 09/06/2011 Next Scheduled EDR Contact: 12/19/2011 Data Release Frequency: No Update Planned TC5146125.2s Page GR-6 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING LUST REG 3: Leaking Underground Storage Tank Database Leaking Underground Storage Tank locations. Monterey, San Benito, San Luis Obispo, Santa Barbara, Santa Cruz counties. Date of Government Version: 05/19/2003 Date Data Arrived at EDR: 05/19/2003 Date Made Active in Reports: 06/02/2003 Number of Days to Update: 14 Source: California Regional Water Quality Control Board Central Coast Region (3) Telephone: 805-542-4786 Last EDR Contact: 07/18/2011 Next Scheduled EDR Contact: 10/31/2011 Data Release Frequency: No Update Planned LUST REG 7: Leaking Underground Storage Tank Case Listing Leaking Underground Storage Tank locations. Imperial, Riverside, San Diego, Santa Barbara counties. Date of Government Version: 02/26/2004 Date Data Arrived at EDR: 02/26/2004 Date Made Active in Reports: 03/24/2004 Number of Days to Update: 27 Source: California Regional Water Quality Control Board Colorado River Basin Region (7) Telephone: 760-776-8943 Last EDR Contact: 08/01/2011 Next Scheduled EDR Contact: 11/14/2011 Data Release Frequency: No Update Planned LUST: Leaking Underground Fuel Tank Report (GEOTRACKER) Leaking Underground Storage Tank (LUST) Sites included in GeoTracker. GeoTracker is the Water Boards data management system for sites that impact, or have the potential to impact, water quality in California, with emphasis on groundwater. Date of Government Version: 09/11/2017 Date Data Arrived at EDR: 09/12/2017 Date Made Active in Reports: 11/09/2017 Number of Days to Update: 58 Source: State Water Resources Control Board Telephone: see region list Last EDR Contact: 12/12/2018 Next Scheduled EDR Contact: 03/26/2018 Data Release Frequency: Quarterly LUST REG 1: Active Toxic Site Investigation Del Norte, Humboldt, Lake, Mendocino, Modoc, Siskiyou, Sonoma, Trinity counties. For more current information, please refer to the State Water Resources Control Board’s LUST database. Date of Government Version: 02/01/2001 Date Data Arrived at EDR: 02/28/2001 Date Made Active in Reports: 03/29/2001 Number of Days to Update: 29 Source: California Regional Water Quality Control Board North Coast (1) Telephone: 707-570-3769 Last EDR Contact: 08/01/2011 Next Scheduled EDR Contact: 11/14/2011 Data Release Frequency: No Update Planned LUST REG 6V: Leaking Underground Storage Tank Case Listing Leaking Underground Storage Tank locations. Inyo, Kern, Los Angeles, Mono, San Bernardino counties. Date of Government Version: 06/07/2005 Date Data Arrived at EDR: 06/07/2005 Date Made Active in Reports: 06/29/2005 Number of Days to Update: 22 Source: California Regional Water Quality Control Board Victorville Branch Office (6) Telephone: 760-241-7365 Last EDR Contact: 09/12/2011 Next Scheduled EDR Contact: 12/26/2011 Data Release Frequency: No Update Planned INDIAN LUST R10: Leaking Underground Storage Tanks on Indian Land LUSTs on Indian land in Alaska, Idaho, Oregon and Washington. Date of Government Version: 04/25/2017 Date Data Arrived at EDR: 11/07/2017 Date Made Active in Reports: 12/08/2017 Number of Days to Update: 31 Source: EPA Region 10 Telephone: 206-553-2857 Last EDR Contact: 11/07/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Varies INDIAN LUST R9: Leaking Underground Storage Tanks on Indian Land LUSTs on Indian land in Arizona, California, New Mexico and Nevada Date of Government Version: 04/13/2017 Date Data Arrived at EDR: 07/27/2017 Date Made Active in Reports: 10/13/2017 Number of Days to Update: 78 Source: Environmental Protection Agency Telephone: 415-972-3372 Last EDR Contact: 10/27/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Varies TC5146125.2s Page GR-7 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING INDIAN LUST R8: Leaking Underground Storage Tanks on Indian Land LUSTs on Indian land in Colorado, Montana, North Dakota, South Dakota, Utah and Wyoming. Date of Government Version: 05/01/2017 Date Data Arrived at EDR: 07/27/2017 Date Made Active in Reports: 10/13/2017 Number of Days to Update: 78 Source: EPA Region 8 Telephone: 303-312-6271 Last EDR Contact: 10/27/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Varies INDIAN LUST R6: Leaking Underground Storage Tanks on Indian Land LUSTs on Indian land in New Mexico and Oklahoma. Date of Government Version: 04/24/2017 Date Data Arrived at EDR: 07/27/2017 Date Made Active in Reports: 10/06/2017 Number of Days to Update: 71 Source: EPA Region 6 Telephone: 214-665-6597 Last EDR Contact: 10/27/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Varies INDIAN LUST R4: Leaking Underground Storage Tanks on Indian Land LUSTs on Indian land in Florida, Mississippi and North Carolina. Date of Government Version: 10/14/2016 Date Data Arrived at EDR: 01/27/2017 Date Made Active in Reports: 05/05/2017 Number of Days to Update: 98 Source: EPA Region 4 Telephone: 404-562-8677 Last EDR Contact: 10/27/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Semi-Annually INDIAN LUST R1: Leaking Underground Storage Tanks on Indian Land A listing of leaking underground storage tank locations on Indian Land. Date of Government Version: 04/14/2017 Date Data Arrived at EDR: 07/27/2017 Date Made Active in Reports: 10/06/2017 Number of Days to Update: 71 Source: EPA Region 1 Telephone: 617-918-1313 Last EDR Contact: 10/27/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Varies INDIAN LUST R5: Leaking Underground Storage Tanks on Indian Land Leaking underground storage tanks located on Indian Land in Michigan, Minnesota and Wisconsin. Date of Government Version: 04/26/2017 Date Data Arrived at EDR: 07/27/2017 Date Made Active in Reports: 10/13/2017 Number of Days to Update: 78 Source: EPA, Region 5 Telephone: 312-886-7439 Last EDR Contact: 10/27/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Varies INDIAN LUST R7: Leaking Underground Storage Tanks on Indian Land LUSTs on Indian land in Iowa, Kansas, and Nebraska Date of Government Version: 04/14/2017 Date Data Arrived at EDR: 07/27/2017 Date Made Active in Reports: 10/06/2017 Number of Days to Update: 71 Source: EPA Region 7 Telephone: 913-551-7003 Last EDR Contact: 10/27/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Varies SLIC: Statewide SLIC Cases (GEOTRACKER) Cleanup Program Sites (CPS; also known as Site Cleanups [SC] and formerly known as Spills, Leaks, Investigations, and Cleanups [SLIC] sites) included in GeoTracker. GeoTracker is the Water Boards data management system for sites that impact, or have the potential to impact, water quality in California, with emphasis on groundwater. Date of Government Version: 09/11/2017 Date Data Arrived at EDR: 09/12/2017 Date Made Active in Reports: 11/09/2017 Number of Days to Update: 58 Source: State Water Resources Control Board Telephone: 866-480-1028 Last EDR Contact: 12/12/2018 Next Scheduled EDR Contact: 03/26/2018 Data Release Frequency: Varies TC5146125.2s Page GR-8 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING SLIC REG 1: Active Toxic Site Investigations The SLIC (Spills, Leaks, Investigations and Cleanup) program is designed to protect and restore water quality from spills, leaks, and similar discharges. Date of Government Version: 04/03/2003 Date Data Arrived at EDR: 04/07/2003 Date Made Active in Reports: 04/25/2003 Number of Days to Update: 18 Source: California Regional Water Quality Control Board, North Coast Region (1) Telephone: 707-576-2220 Last EDR Contact: 08/01/2011 Next Scheduled EDR Contact: 11/14/2011 Data Release Frequency: No Update Planned SLIC REG 2: Spills, Leaks, Investigation & Cleanup Cost Recovery Listing The SLIC (Spills, Leaks, Investigations and Cleanup) program is designed to protect and restore water quality from spills, leaks, and similar discharges. Date of Government Version: 09/30/2004 Date Data Arrived at EDR: 10/20/2004 Date Made Active in Reports: 11/19/2004 Number of Days to Update: 30 Source: Regional Water Quality Control Board San Francisco Bay Region (2) Telephone: 510-286-0457 Last EDR Contact: 09/19/2011 Next Scheduled EDR Contact: 01/02/2012 Data Release Frequency: Quarterly SLIC REG 3: Spills, Leaks, Investigation & Cleanup Cost Recovery Listing The SLIC (Spills, Leaks, Investigations and Cleanup) program is designed to protect and restore water quality from spills, leaks, and similar discharges. Date of Government Version: 05/18/2006 Date Data Arrived at EDR: 05/18/2006 Date Made Active in Reports: 06/15/2006 Number of Days to Update: 28 Source: California Regional Water Quality Control Board Central Coast Region (3) Telephone: 805-549-3147 Last EDR Contact: 07/18/2011 Next Scheduled EDR Contact: 10/31/2011 Data Release Frequency: Semi-Annually SLIC REG 4: Spills, Leaks, Investigation & Cleanup Cost Recovery Listing The SLIC (Spills, Leaks, Investigations and Cleanup) program is designed to protect and restore water quality from spills, leaks, and similar discharges. Date of Government Version: 11/17/2004 Date Data Arrived at EDR: 11/18/2004 Date Made Active in Reports: 01/04/2005 Number of Days to Update: 47 Source: Region Water Quality Control Board Los Angeles Region (4) Telephone: 213-576-6600 Last EDR Contact: 07/01/2011 Next Scheduled EDR Contact: 10/17/2011 Data Release Frequency: Varies SLIC REG 5: Spills, Leaks, Investigation & Cleanup Cost Recovery Listing The SLIC (Spills, Leaks, Investigations and Cleanup) program is designed to protect and restore water quality from spills, leaks, and similar discharges. Date of Government Version: 04/01/2005 Date Data Arrived at EDR: 04/05/2005 Date Made Active in Reports: 04/21/2005 Number of Days to Update: 16 Source: Regional Water Quality Control Board Central Valley Region (5) Telephone: 916-464-3291 Last EDR Contact: 09/12/2011 Next Scheduled EDR Contact: 12/26/2011 Data Release Frequency: Semi-Annually SLIC REG 6V: Spills, Leaks, Investigation & Cleanup Cost Recovery Listing The SLIC (Spills, Leaks, Investigations and Cleanup) program is designed to protect and restore water quality from spills, leaks, and similar discharges. Date of Government Version: 05/24/2005 Date Data Arrived at EDR: 05/25/2005 Date Made Active in Reports: 06/16/2005 Number of Days to Update: 22 Source: Regional Water Quality Control Board, Victorville Branch Telephone: 619-241-6583 Last EDR Contact: 08/15/2011 Next Scheduled EDR Contact: 11/28/2011 Data Release Frequency: Semi-Annually TC5146125.2s Page GR-9 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING SLIC REG 6L: SLIC Sites The SLIC (Spills, Leaks, Investigations and Cleanup) program is designed to protect and restore water quality from spills, leaks, and similar discharges. Date of Government Version: 09/07/2004 Date Data Arrived at EDR: 09/07/2004 Date Made Active in Reports: 10/12/2004 Number of Days to Update: 35 Source: California Regional Water Quality Control Board, Lahontan Region Telephone: 530-542-5574 Last EDR Contact: 08/15/2011 Next Scheduled EDR Contact: 11/28/2011 Data Release Frequency: No Update Planned SLIC REG 7: SLIC List The SLIC (Spills, Leaks, Investigations and Cleanup) program is designed to protect and restore water quality from spills, leaks, and similar discharges. Date of Government Version: 11/24/2004 Date Data Arrived at EDR: 11/29/2004 Date Made Active in Reports: 01/04/2005 Number of Days to Update: 36 Source: California Regional Quality Control Board, Colorado River Basin Region Telephone: 760-346-7491 Last EDR Contact: 08/01/2011 Next Scheduled EDR Contact: 11/14/2011 Data Release Frequency: No Update Planned SLIC REG 8: Spills, Leaks, Investigation & Cleanup Cost Recovery Listing The SLIC (Spills, Leaks, Investigations and Cleanup) program is designed to protect and restore water quality from spills, leaks, and similar discharges. Date of Government Version: 04/03/2008 Date Data Arrived at EDR: 04/03/2008 Date Made Active in Reports: 04/14/2008 Number of Days to Update: 11 Source: California Region Water Quality Control Board Santa Ana Region (8) Telephone: 951-782-3298 Last EDR Contact: 09/12/2011 Next Scheduled EDR Contact: 12/26/2011 Data Release Frequency: Semi-Annually SLIC REG 9: Spills, Leaks, Investigation & Cleanup Cost Recovery Listing The SLIC (Spills, Leaks, Investigations and Cleanup) program is designed to protect and restore water quality from spills, leaks, and similar discharges. Date of Government Version: 09/10/2007 Date Data Arrived at EDR: 09/11/2007 Date Made Active in Reports: 09/28/2007 Number of Days to Update: 17 Source: California Regional Water Quality Control Board San Diego Region (9) Telephone: 858-467-2980 Last EDR Contact: 08/08/2011 Next Scheduled EDR Contact: 11/21/2011 Data Release Frequency: Annually State and tribal registered storage tank lists FEMA UST: Underground Storage Tank Listing A listing of all FEMA owned underground storage tanks. Date of Government Version: 05/15/2017 Date Data Arrived at EDR: 05/30/2017 Date Made Active in Reports: 10/13/2017 Number of Days to Update: 136 Source: FEMA Telephone: 202-646-5797 Last EDR Contact: 10/13/2017 Next Scheduled EDR Contact: 01/22/2018 Data Release Frequency: Varies UST: Active UST Facilities Active UST facilities gathered from the local regulatory agencies Date of Government Version: 09/11/2017 Date Data Arrived at EDR: 09/12/2017 Date Made Active in Reports: 11/08/2017 Number of Days to Update: 57 Source: SWRCB Telephone: 916-341-5851 Last EDR Contact: 12/12/2017 Next Scheduled EDR Contact: 03/26/2018 Data Release Frequency: Semi-Annually TC5146125.2s Page GR-10 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING AST: Aboveground Petroleum Storage Tank Facilities A listing of aboveground storage tank petroleum storage tank locations. Date of Government Version: 07/06/2016 Date Data Arrived at EDR: 07/12/2016 Date Made Active in Reports: 09/19/2016 Number of Days to Update: 69 Source: California Environmental Protection Agency Telephone: 916-327-5092 Last EDR Contact: 09/25/2017 Next Scheduled EDR Contact: 01/08/2018 Data Release Frequency: Quarterly INDIAN UST R5: Underground Storage Tanks on Indian Land The Indian Underground Storage Tank (UST) database provides information about underground storage tanks on Indian land in EPA Region 5 (Michigan, Minnesota and Wisconsin and Tribal Nations). Date of Government Version: 04/26/2017 Date Data Arrived at EDR: 07/27/2017 Date Made Active in Reports: 10/06/2017 Number of Days to Update: 71 Source: EPA Region 5 Telephone: 312-886-6136 Last EDR Contact: 10/27/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Varies INDIAN UST R6: Underground Storage Tanks on Indian Land The Indian Underground Storage Tank (UST) database provides information about underground storage tanks on Indian land in EPA Region 6 (Louisiana, Arkansas, Oklahoma, New Mexico, Texas and 65 Tribes). Date of Government Version: 04/24/2017 Date Data Arrived at EDR: 07/27/2017 Date Made Active in Reports: 12/08/2017 Number of Days to Update: 134 Source: EPA Region 6 Telephone: 214-665-7591 Last EDR Contact: 10/27/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Varies INDIAN UST R7: Underground Storage Tanks on Indian Land The Indian Underground Storage Tank (UST) database provides information about underground storage tanks on Indian land in EPA Region 7 (Iowa, Kansas, Missouri, Nebraska, and 9 Tribal Nations). Date of Government Version: 05/02/2017 Date Data Arrived at EDR: 07/27/2017 Date Made Active in Reports: 10/06/2017 Number of Days to Update: 71 Source: EPA Region 7 Telephone: 913-551-7003 Last EDR Contact: 10/27/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Varies INDIAN UST R8: Underground Storage Tanks on Indian Land The Indian Underground Storage Tank (UST) database provides information about underground storage tanks on Indian land in EPA Region 8 (Colorado, Montana, North Dakota, South Dakota, Utah, Wyoming and 27 Tribal Nations). Date of Government Version: 05/01/2017 Date Data Arrived at EDR: 07/27/2017 Date Made Active in Reports: 10/13/2017 Number of Days to Update: 78 Source: EPA Region 8 Telephone: 303-312-6137 Last EDR Contact: 10/27/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Varies INDIAN UST R9: Underground Storage Tanks on Indian Land The Indian Underground Storage Tank (UST) database provides information about underground storage tanks on Indian land in EPA Region 9 (Arizona, California, Hawaii, Nevada, the Pacific Islands, and Tribal Nations). Date of Government Version: 04/13/2017 Date Data Arrived at EDR: 07/27/2017 Date Made Active in Reports: 10/13/2017 Number of Days to Update: 78 Source: EPA Region 9 Telephone: 415-972-3368 Last EDR Contact: 10/27/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Varies TC5146125.2s Page GR-11 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING INDIAN UST R4: Underground Storage Tanks on Indian Land The Indian Underground Storage Tank (UST) database provides information about underground storage tanks on Indian land in EPA Region 4 (Alabama, Florida, Georgia, Kentucky, Mississippi, North Carolina, South Carolina, Tennessee and Tribal Nations) Date of Government Version: 10/14/2016 Date Data Arrived at EDR: 01/27/2017 Date Made Active in Reports: 05/05/2017 Number of Days to Update: 98 Source: EPA Region 4 Telephone: 404-562-9424 Last EDR Contact: 10/27/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Semi-Annually INDIAN UST R1: Underground Storage Tanks on Indian Land The Indian Underground Storage Tank (UST) database provides information about underground storage tanks on Indian land in EPA Region 1 (Connecticut, Maine, Massachusetts, New Hampshire, Rhode Island, Vermont and ten Tribal Nations). Date of Government Version: 04/14/2017 Date Data Arrived at EDR: 07/27/2017 Date Made Active in Reports: 10/06/2017 Number of Days to Update: 71 Source: EPA, Region 1 Telephone: 617-918-1313 Last EDR Contact: 10/27/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Varies INDIAN UST R10: Underground Storage Tanks on Indian Land The Indian Underground Storage Tank (UST) database provides information about underground storage tanks on Indian land in EPA Region 10 (Alaska, Idaho, Oregon, Washington, and Tribal Nations). Date of Government Version: 04/25/2017 Date Data Arrived at EDR: 07/27/2017 Date Made Active in Reports: 10/13/2017 Number of Days to Update: 78 Source: EPA Region 10 Telephone: 206-553-2857 Last EDR Contact: 10/27/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Varies State and tribal voluntary cleanup sites VCP: Voluntary Cleanup Program Properties Contains low threat level properties with either confirmed or unconfirmed releases and the project proponents have request that DTSC oversee investigation and/or cleanup activities and have agreed to provide coverage for DTSC’s costs. Date of Government Version: 10/30/2017 Date Data Arrived at EDR: 10/31/2017 Date Made Active in Reports: 12/15/2017 Number of Days to Update: 45 Source: Department of Toxic Substances Control Telephone: 916-323-3400 Last EDR Contact: 10/31/2017 Next Scheduled EDR Contact: 02/12/2018 Data Release Frequency: Quarterly INDIAN VCP R7: Voluntary Cleanup Priority Lisitng A listing of voluntary cleanup priority sites located on Indian Land located in Region 7. Date of Government Version: 03/20/2008 Date Data Arrived at EDR: 04/22/2008 Date Made Active in Reports: 05/19/2008 Number of Days to Update: 27 Source: EPA, Region 7 Telephone: 913-551-7365 Last EDR Contact: 04/20/2009 Next Scheduled EDR Contact: 07/20/2009 Data Release Frequency: Varies INDIAN VCP R1: Voluntary Cleanup Priority Listing A listing of voluntary cleanup priority sites located on Indian Land located in Region 1. Date of Government Version: 07/27/2015 Date Data Arrived at EDR: 09/29/2015 Date Made Active in Reports: 02/18/2016 Number of Days to Update: 142 Source: EPA, Region 1 Telephone: 617-918-1102 Last EDR Contact: 12/20/2017 Next Scheduled EDR Contact: 04/09/2018 Data Release Frequency: Varies TC5146125.2s Page GR-12 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING State and tribal Brownfields sites BROWNFIELDS: Considered Brownfieds Sites Listing A listing of sites the SWRCB considers to be Brownfields since these are sites have come to them through the MOA Process. Date of Government Version: 09/21/2017 Date Data Arrived at EDR: 09/21/2017 Date Made Active in Reports: 11/09/2017 Number of Days to Update: 49 Source: State Water Resources Control Board Telephone: 916-323-7905 Last EDR Contact: 09/21/2017 Next Scheduled EDR Contact: 01/08/2018 Data Release Frequency: Quarterly ADDITIONAL ENVIRONMENTAL RECORDS Local Brownfield lists US BROWNFIELDS: A Listing of Brownfields Sites Brownfields are real property, the expansion, redevelopment, or reuse of which may be complicated by the presence or potential presence of a hazardous substance, pollutant, or contaminant. Cleaning up and reinvesting in these properties takes development pressures off of undeveloped, open land, and both improves and protects the environment. Assessment, Cleanup and Redevelopment Exchange System (ACRES) stores information reported by EPA Brownfields grant recipients on brownfields properties assessed or cleaned up with grant funding as well as information on Targeted Brownfields Assessments performed by EPA Regions. A listing of ACRES Brownfield sites is obtained from Cleanups in My Community. Cleanups in My Community provides information on Brownfields properties for which information is reported back to EPA, as well as areas served by Brownfields grant programs. Date of Government Version: 08/21/2017 Date Data Arrived at EDR: 09/20/2017 Date Made Active in Reports: 12/08/2017 Number of Days to Update: 79 Source: Environmental Protection Agency Telephone: 202-566-2777 Last EDR Contact: 12/19/2017 Next Scheduled EDR Contact: 04/02/2018 Data Release Frequency: Semi-Annually Local Lists of Landfill / Solid Waste Disposal Sites WMUDS/SWAT: Waste Management Unit Database Waste Management Unit Database System. WMUDS is used by the State Water Resources Control Board staff and the Regional Water Quality Control Boards for program tracking and inventory of waste management units. WMUDS is composed of the following databases: Facility Information, Scheduled Inspections Information, Waste Management Unit Information, SWAT Program Information, SWAT Report Summary Information, SWAT Report Summary Data, Chapter 15 (formerly Subchapter 15) Information, Chapter 15 Monitoring Parameters, TPCA Program Information, RCRA Program Information, Closure Information, and Interested Parties Information. Date of Government Version: 04/01/2000 Date Data Arrived at EDR: 04/10/2000 Date Made Active in Reports: 05/10/2000 Number of Days to Update: 30 Source: State Water Resources Control Board Telephone: 916-227-4448 Last EDR Contact: 11/06/2017 Next Scheduled EDR Contact: 02/19/2018 Data Release Frequency: No Update Planned SWRCY: Recycler Database A listing of recycling facilities in California. Date of Government Version: 09/11/2017 Date Data Arrived at EDR: 09/12/2017 Date Made Active in Reports: 09/21/2017 Number of Days to Update: 9 Source: Department of Conservation Telephone: 916-323-3836 Last EDR Contact: 12/12/2017 Next Scheduled EDR Contact: 03/26/2018 Data Release Frequency: Quarterly HAULERS: Registered Waste Tire Haulers Listing A listing of registered waste tire haulers. TC5146125.2s Page GR-13 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Date of Government Version: 05/30/2017 Date Data Arrived at EDR: 05/31/2017 Date Made Active in Reports: 08/15/2017 Number of Days to Update: 76 Source: Integrated Waste Management Board Telephone: 916-341-6422 Last EDR Contact: 11/09/2017 Next Scheduled EDR Contact: 02/26/2018 Data Release Frequency: Varies INDIAN ODI: Report on the Status of Open Dumps on Indian Lands Location of open dumps on Indian land. Date of Government Version: 12/31/1998 Date Data Arrived at EDR: 12/03/2007 Date Made Active in Reports: 01/24/2008 Number of Days to Update: 52 Source: Environmental Protection Agency Telephone: 703-308-8245 Last EDR Contact: 10/30/2017 Next Scheduled EDR Contact: 02/12/2018 Data Release Frequency: Varies ODI: Open Dump Inventory An open dump is defined as a disposal facility that does not comply with one or more of the Part 257 or Part 258 Subtitle D Criteria. Date of Government Version: 06/30/1985 Date Data Arrived at EDR: 08/09/2004 Date Made Active in Reports: 09/17/2004 Number of Days to Update: 39 Source: Environmental Protection Agency Telephone: 800-424-9346 Last EDR Contact: 06/09/2004 Next Scheduled EDR Contact: N/A Data Release Frequency: No Update Planned DEBRIS REGION 9: Torres Martinez Reservation Illegal Dump Site Locations A listing of illegal dump sites location on the Torres Martinez Indian Reservation located in eastern Riverside County and northern Imperial County, California. Date of Government Version: 01/12/2009 Date Data Arrived at EDR: 05/07/2009 Date Made Active in Reports: 09/21/2009 Number of Days to Update: 137 Source: EPA, Region 9 Telephone: 415-947-4219 Last EDR Contact: 10/20/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: No Update Planned IHS OPEN DUMPS: Open Dumps on Indian Land A listing of all open dumps located on Indian Land in the United States. Date of Government Version: 04/01/2014 Date Data Arrived at EDR: 08/06/2014 Date Made Active in Reports: 01/29/2015 Number of Days to Update: 176 Source: Department of Health & Human Serivces, Indian Health Service Telephone: 301-443-1452 Last EDR Contact: 11/03/2017 Next Scheduled EDR Contact: 02/12/2018 Data Release Frequency: Varies Local Lists of Hazardous waste / Contaminated Sites US HIST CDL: National Clandestine Laboratory Register A listing of clandestine drug lab locations that have been removed from the DEAs National Clandestine Laboratory Register. Date of Government Version: 07/13/2017 Date Data Arrived at EDR: 09/06/2017 Date Made Active in Reports: 10/06/2017 Number of Days to Update: 30 Source: Drug Enforcement Administration Telephone: 202-307-1000 Last EDR Contact: 11/28/2017 Next Scheduled EDR Contact: 03/12/2018 Data Release Frequency: No Update Planned HIST CAL-SITES: Calsites Database The Calsites database contains potential or confirmed hazardous substance release properties. In 1996, California EPA reevaluated and significantly reduced the number of sites in the Calsites database. No longer updated by the state agency. It has been replaced by ENVIROSTOR. TC5146125.2s Page GR-14 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Date of Government Version: 08/08/2005 Date Data Arrived at EDR: 08/03/2006 Date Made Active in Reports: 08/24/2006 Number of Days to Update: 21 Source: Department of Toxic Substance Control Telephone: 916-323-3400 Last EDR Contact: 02/23/2009 Next Scheduled EDR Contact: 05/25/2009 Data Release Frequency: No Update Planned SCH: School Property Evaluation Program This category contains proposed and existing school sites that are being evaluated by DTSC for possible hazardous materials contamination. In some cases, these properties may be listed in the CalSites category depending on the level of threat to public health and safety or the environment they pose. Date of Government Version: 10/30/2017 Date Data Arrived at EDR: 10/31/2017 Date Made Active in Reports: 12/15/2017 Number of Days to Update: 45 Source: Department of Toxic Substances Control Telephone: 916-323-3400 Last EDR Contact: 10/31/2017 Next Scheduled EDR Contact: 02/12/2018 Data Release Frequency: Quarterly CDL: Clandestine Drug Labs A listing of drug lab locations. Listing of a location in this database does not indicate that any illegal drug lab materials were or were not present there, and does not constitute a determination that the location either requires or does not require additional cleanup work. Date of Government Version: 06/30/2017 Date Data Arrived at EDR: 08/18/2017 Date Made Active in Reports: 09/21/2017 Number of Days to Update: 34 Source: Department of Toxic Substances Control Telephone: 916-255-6504 Last EDR Contact: 10/10/2017 Next Scheduled EDR Contact: 01/22/2018 Data Release Frequency: Varies TOXIC PITS: Toxic Pits Cleanup Act Sites Toxic PITS Cleanup Act Sites. TOXIC PITS identifies sites suspected of containing hazardous substances where cleanup has not yet been completed. Date of Government Version: 07/01/1995 Date Data Arrived at EDR: 08/30/1995 Date Made Active in Reports: 09/26/1995 Number of Days to Update: 27 Source: State Water Resources Control Board Telephone: 916-227-4364 Last EDR Contact: 01/26/2009 Next Scheduled EDR Contact: 04/27/2009 Data Release Frequency: No Update Planned US CDL: Clandestine Drug Labs A listing of clandestine drug lab locations. The U.S. Department of Justice ("the Department") provides this web site as a public service. It contains addresses of some locations where law enforcement agencies reported they found chemicals or other items that indicated the presence of either clandestine drug laboratories or dumpsites. In most cases, the source of the entries is not the Department, and the Department has not verified the entry and does not guarantee its accuracy. Members of the public must verify the accuracy of all entries by, for example, contacting local law enforcement and local health departments. Date of Government Version: 07/13/2017 Date Data Arrived at EDR: 09/06/2017 Date Made Active in Reports: 10/06/2017 Number of Days to Update: 30 Source: Drug Enforcement Administration Telephone: 202-307-1000 Last EDR Contact: 11/28/2017 Next Scheduled EDR Contact: 03/12/2018 Data Release Frequency: Quarterly Local Lists of Registered Storage Tanks SWEEPS UST: SWEEPS UST Listing Statewide Environmental Evaluation and Planning System. This underground storage tank listing was updated and maintained by a company contacted by the SWRCB in the early 1990’s. The listing is no longer updated or maintained. The local agency is the contact for more information on a site on the SWEEPS list. TC5146125.2s Page GR-15 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Date of Government Version: 06/01/1994 Date Data Arrived at EDR: 07/07/2005 Date Made Active in Reports: 08/11/2005 Number of Days to Update: 35 Source: State Water Resources Control Board Telephone: N/A Last EDR Contact: 06/03/2005 Next Scheduled EDR Contact: N/A Data Release Frequency: No Update Planned UST MENDOCINO: Mendocino County UST Database A listing of underground storage tank locations in Mendocino County. Date of Government Version: 11/27/2017 Date Data Arrived at EDR: 11/29/2017 Date Made Active in Reports: 12/18/2017 Number of Days to Update: 19 Source: Department of Public Health Telephone: 707-463-4466 Last EDR Contact: 11/28/2017 Next Scheduled EDR Contact: 03/12/2018 Data Release Frequency: Annually HIST UST: Hazardous Substance Storage Container Database The Hazardous Substance Storage Container Database is a historical listing of UST sites. Refer to local/county source for current data. Date of Government Version: 10/15/1990 Date Data Arrived at EDR: 01/25/1991 Date Made Active in Reports: 02/12/1991 Number of Days to Update: 18 Source: State Water Resources Control Board Telephone: 916-341-5851 Last EDR Contact: 07/26/2001 Next Scheduled EDR Contact: N/A Data Release Frequency: No Update Planned CA FID UST: Facility Inventory Database The Facility Inventory Database (FID) contains a historical listing of active and inactive underground storage tank locations from the State Water Resource Control Board. Refer to local/county source for current data. Date of Government Version: 10/31/1994 Date Data Arrived at EDR: 09/05/1995 Date Made Active in Reports: 09/29/1995 Number of Days to Update: 24 Source: California Environmental Protection Agency Telephone: 916-341-5851 Last EDR Contact: 12/28/1998 Next Scheduled EDR Contact: N/A Data Release Frequency: No Update Planned Local Land Records LIENS: Environmental Liens Listing A listing of property locations with environmental liens for California where DTSC is a lien holder. Date of Government Version: 08/31/2017 Date Data Arrived at EDR: 09/05/2017 Date Made Active in Reports: 11/08/2017 Number of Days to Update: 64 Source: Department of Toxic Substances Control Telephone: 916-323-3400 Last EDR Contact: 11/30/2017 Next Scheduled EDR Contact: 03/19/2018 Data Release Frequency: Varies LIENS 2: CERCLA Lien Information A Federal CERCLA (’Superfund’) lien can exist by operation of law at any site or property at which EPA has spent Superfund monies. These monies are spent to investigate and address releases and threatened releases of contamination. CERCLIS provides information as to the identity of these sites and properties. Date of Government Version: 07/11/2017 Date Data Arrived at EDR: 07/26/2017 Date Made Active in Reports: 10/13/2017 Number of Days to Update: 79 Source: Environmental Protection Agency Telephone: 202-564-6023 Last EDR Contact: 12/22/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Semi-Annually DEED: Deed Restriction Listing TC5146125.2s Page GR-16 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Site Mitigation and Brownfields Reuse Program Facility Sites with Deed Restrictions & Hazardous Waste Management Program Facility Sites with Deed / Land Use Restriction. The DTSC Site Mitigation and Brownfields Reuse Program SMBRP) list includes sites cleaned up under the program’s oversight and generally does not include current or former hazardous waste facilities that required a hazardous waste facility permit. The list represents deed restrictions that are active. Some sites have multiple deed restrictions. The DTSC Hazardous Waste Management Program (HWMP) has developed a list of current or former hazardous waste facilities that have a recorded land use restriction at the local county recorder’s office. The land use restrictions on this list were required by the DTSC HWMP as a result of the presence of hazardous substances that remain on site after the facility (or part of the facility) has been closed or cleaned up. The types of land use restriction include deed notice, deed restriction, or a land use restriction that binds current and future owners. Date of Government Version: 09/05/2017 Date Data Arrived at EDR: 09/06/2017 Date Made Active in Reports: 11/08/2017 Number of Days to Update: 63 Source: DTSC and SWRCB Telephone: 916-323-3400 Last EDR Contact: 12/05/2017 Next Scheduled EDR Contact: 03/19/2018 Data Release Frequency: Semi-Annually Records of Emergency Release Reports HMIRS: Hazardous Materials Information Reporting System Hazardous Materials Incident Report System. HMIRS contains hazardous material spill incidents reported to DOT. Date of Government Version: 09/21/2017 Date Data Arrived at EDR: 09/21/2017 Date Made Active in Reports: 10/13/2017 Number of Days to Update: 22 Source: U.S. Department of Transportation Telephone: 202-366-4555 Last EDR Contact: 09/21/2017 Next Scheduled EDR Contact: 01/08/2018 Data Release Frequency: Quarterly CHMIRS: California Hazardous Material Incident Report System California Hazardous Material Incident Reporting System. CHMIRS contains information on reported hazardous material incidents (accidental releases or spills). Date of Government Version: 05/09/2017 Date Data Arrived at EDR: 07/26/2017 Date Made Active in Reports: 09/21/2017 Number of Days to Update: 57 Source: Office of Emergency Services Telephone: 916-845-8400 Last EDR Contact: 10/27/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Varies LDS: Land Disposal Sites Listing (GEOTRACKER) Land Disposal sites (Landfills) included in GeoTracker. GeoTracker is the Water Boards data management system for sites that impact, or have the potential to impact, water quality in California, with emphasis on groundwater. Date of Government Version: 09/11/2017 Date Data Arrived at EDR: 09/12/2017 Date Made Active in Reports: 11/09/2017 Number of Days to Update: 58 Source: State Water Qualilty Control Board Telephone: 866-480-1028 Last EDR Contact: 12/12/2018 Next Scheduled EDR Contact: 03/26/2018 Data Release Frequency: Quarterly MCS: Military Cleanup Sites Listing (GEOTRACKER) Military sites (consisting of: Military UST sites; Military Privatized sites; and Military Cleanup sites [formerly known as DoD non UST]) included in GeoTracker. GeoTracker is the Water Boards data management system for sites that impact, or have the potential to impact, water quality in California, with emphasis on groundwater. Date of Government Version: 09/11/2017 Date Data Arrived at EDR: 09/12/2017 Date Made Active in Reports: 11/09/2017 Number of Days to Update: 58 Source: State Water Resources Control Board Telephone: 866-480-1028 Last EDR Contact: 12/12/2018 Next Scheduled EDR Contact: 03/26/2018 Data Release Frequency: Quarterly TC5146125.2s Page GR-17 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING SPILLS 90: SPILLS90 data from FirstSearch Spills 90 includes those spill and release records available exclusively from FirstSearch databases. Typically, they may include chemical, oil and/or hazardous substance spills recorded after 1990. Duplicate records that are already included in EDR incident and release records are not included in Spills 90. Date of Government Version: 06/06/2012 Date Data Arrived at EDR: 01/03/2013 Date Made Active in Reports: 02/22/2013 Number of Days to Update: 50 Source: FirstSearch Telephone: N/A Last EDR Contact: 01/03/2013 Next Scheduled EDR Contact: N/A Data Release Frequency: No Update Planned Other Ascertainable Records RCRA NonGen / NLR: RCRA - Non Generators / No Longer Regulated RCRAInfo is EPA’s comprehensive information system, providing access to data supporting the Resource Conservation and Recovery Act (RCRA) of 1976 and the Hazardous and Solid Waste Amendments (HSWA) of 1984. The database includes selective information on sites which generate, transport, store, treat and/or dispose of hazardous waste as defined by the Resource Conservation and Recovery Act (RCRA). Non-Generators do not presently generate hazardous waste. Date of Government Version: 09/13/2017 Date Data Arrived at EDR: 09/26/2017 Date Made Active in Reports: 10/06/2017 Number of Days to Update: 10 Source: Environmental Protection Agency Telephone: (415) 495-8895 Last EDR Contact: 09/26/2017 Next Scheduled EDR Contact: 01/08/2018 Data Release Frequency: Quarterly FUDS: Formerly Used Defense Sites The listing includes locations of Formerly Used Defense Sites properties where the US Army Corps of Engineers is actively working or will take necessary cleanup actions. Date of Government Version: 01/31/2015 Date Data Arrived at EDR: 07/08/2015 Date Made Active in Reports: 10/13/2015 Number of Days to Update: 97 Source: U.S. Army Corps of Engineers Telephone: 202-528-4285 Last EDR Contact: 11/22/2017 Next Scheduled EDR Contact: 03/05/2018 Data Release Frequency: Varies DOD: Department of Defense Sites This data set consists of federally owned or administered lands, administered by the Department of Defense, that have any area equal to or greater than 640 acres of the United States, Puerto Rico, and the U.S. Virgin Islands. Date of Government Version: 12/31/2005 Date Data Arrived at EDR: 11/10/2006 Date Made Active in Reports: 01/11/2007 Number of Days to Update: 62 Source: USGS Telephone: 888-275-8747 Last EDR Contact: 10/13/2017 Next Scheduled EDR Contact: 01/22/2018 Data Release Frequency: Semi-Annually FEDLAND: Federal and Indian Lands Federally and Indian administrated lands of the United States. Lands included are administrated by: Army Corps of Engineers, Bureau of Reclamation, National Wild and Scenic River, National Wildlife Refuge, Public Domain Land, Wilderness, Wilderness Study Area, Wildlife Management Area, Bureau of Indian Affairs, Bureau of Land Management, Department of Justice, Forest Service, Fish and Wildlife Service, National Park Service. Date of Government Version: 12/31/2005 Date Data Arrived at EDR: 02/06/2006 Date Made Active in Reports: 01/11/2007 Number of Days to Update: 339 Source: U.S. Geological Survey Telephone: 888-275-8747 Last EDR Contact: 10/11/2017 Next Scheduled EDR Contact: 01/22/2018 Data Release Frequency: N/A SCRD DRYCLEANERS: State Coalition for Remediation of Drycleaners Listing The State Coalition for Remediation of Drycleaners was established in 1998, with support from the U.S. EPA Office of Superfund Remediation and Technology Innovation. It is comprised of representatives of states with established drycleaner remediation programs. Currently the member states are Alabama, Connecticut, Florida, Illinois, Kansas, Minnesota, Missouri, North Carolina, Oregon, South Carolina, Tennessee, Texas, and Wisconsin. TC5146125.2s Page GR-18 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Date of Government Version: 01/01/2017 Date Data Arrived at EDR: 02/03/2017 Date Made Active in Reports: 04/07/2017 Number of Days to Update: 63 Source: Environmental Protection Agency Telephone: 615-532-8599 Last EDR Contact: 11/17/2017 Next Scheduled EDR Contact: 02/26/2018 Data Release Frequency: Varies US FIN ASSUR: Financial Assurance Information All owners and operators of facilities that treat, store, or dispose of hazardous waste are required to provide proof that they will have sufficient funds to pay for the clean up, closure, and post-closure care of their facilities. Date of Government Version: 10/17/2017 Date Data Arrived at EDR: 11/01/2017 Date Made Active in Reports: 12/08/2017 Number of Days to Update: 37 Source: Environmental Protection Agency Telephone: 202-566-1917 Last EDR Contact: 11/01/2017 Next Scheduled EDR Contact: 01/08/2018 Data Release Frequency: Quarterly EPA WATCH LIST: EPA WATCH LIST EPA maintains a "Watch List" to facilitate dialogue between EPA, state and local environmental agencies on enforcement matters relating to facilities with alleged violations identified as either significant or high priority. Being on the Watch List does not mean that the facility has actually violated the law only that an investigation by EPA or a state or local environmental agency has led those organizations to allege that an unproven violation has in fact occurred. Being on the Watch List does not represent a higher level of concern regarding the alleged violations that were detected, but instead indicates cases requiring additional dialogue between EPA, state and local agencies - primarily because of the length of time the alleged violation has gone unaddressed or unresolved. Date of Government Version: 08/30/2013 Date Data Arrived at EDR: 03/21/2014 Date Made Active in Reports: 06/17/2014 Number of Days to Update: 88 Source: Environmental Protection Agency Telephone: 617-520-3000 Last EDR Contact: 11/06/2017 Next Scheduled EDR Contact: 02/19/2018 Data Release Frequency: Quarterly 2020 COR ACTION: 2020 Corrective Action Program List The EPA has set ambitious goals for the RCRA Corrective Action program by creating the 2020 Corrective Action Universe. This RCRA cleanup baseline includes facilities expected to need corrective action. The 2020 universe contains a wide variety of sites. Some properties are heavily contaminated while others were contaminated but have since been cleaned up. Still others have not been fully investigated yet, and may require little or no remediation. Inclusion in the 2020 Universe does not necessarily imply failure on the part of a facility to meet its RCRA obligations. Date of Government Version: 04/22/2013 Date Data Arrived at EDR: 03/03/2015 Date Made Active in Reports: 03/09/2015 Number of Days to Update: 6 Source: Environmental Protection Agency Telephone: 703-308-4044 Last EDR Contact: 11/09/2017 Next Scheduled EDR Contact: 02/19/2018 Data Release Frequency: Varies TSCA: Toxic Substances Control Act Toxic Substances Control Act. TSCA identifies manufacturers and importers of chemical substances included on the TSCA Chemical Substance Inventory list. It includes data on the production volume of these substances by plant site. Date of Government Version: 12/31/2012 Date Data Arrived at EDR: 01/15/2015 Date Made Active in Reports: 01/29/2015 Number of Days to Update: 14 Source: EPA Telephone: 202-260-5521 Last EDR Contact: 12/22/2017 Next Scheduled EDR Contact: 04/02/2018 Data Release Frequency: Every 4 Years TRIS: Toxic Chemical Release Inventory System Toxic Release Inventory System. TRIS identifies facilities which release toxic chemicals to the air, water and land in reportable quantities under SARA Title III Section 313. TC5146125.2s Page GR-19 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Date of Government Version: 12/31/2014 Date Data Arrived at EDR: 11/24/2015 Date Made Active in Reports: 04/05/2016 Number of Days to Update: 133 Source: EPA Telephone: 202-566-0250 Last EDR Contact: 11/20/2017 Next Scheduled EDR Contact: 03/05/2018 Data Release Frequency: Annually SSTS: Section 7 Tracking Systems Section 7 of the Federal Insecticide, Fungicide and Rodenticide Act, as amended (92 Stat. 829) requires all registered pesticide-producing establishments to submit a report to the Environmental Protection Agency by March 1st each year. Each establishment must report the types and amounts of pesticides, active ingredients and devices being produced, and those having been produced and sold or distributed in the past year. Date of Government Version: 12/31/2009 Date Data Arrived at EDR: 12/10/2010 Date Made Active in Reports: 02/25/2011 Number of Days to Update: 77 Source: EPA Telephone: 202-564-4203 Last EDR Contact: 10/27/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Annually ROD: Records Of Decision Record of Decision. ROD documents mandate a permanent remedy at an NPL (Superfund) site containing technical and health information to aid in the cleanup. Date of Government Version: 09/27/2017 Date Data Arrived at EDR: 10/12/2017 Date Made Active in Reports: 10/20/2017 Number of Days to Update: 8 Source: EPA Telephone: 703-416-0223 Last EDR Contact: 12/22/2017 Next Scheduled EDR Contact: 03/19/2018 Data Release Frequency: Annually RMP: Risk Management Plans When Congress passed the Clean Air Act Amendments of 1990, it required EPA to publish regulations and guidance for chemical accident prevention at facilities using extremely hazardous substances. The Risk Management Program Rule (RMP Rule) was written to implement Section 112(r) of these amendments. The rule, which built upon existing industry codes and standards, requires companies of all sizes that use certain flammable and toxic substances to develop a Risk Management Program, which includes a(n): Hazard assessment that details the potential effects of an accidental release, an accident history of the last five years, and an evaluation of worst-case and alternative accidental releases; Prevention program that includes safety precautions and maintenance, monitoring, and employee training measures; and Emergency response program that spells out emergency health care, employee training measures and procedures for informing the public and response agencies (e.g the fire department) should an accident occur. Date of Government Version: 11/02/2017 Date Data Arrived at EDR: 11/17/2017 Date Made Active in Reports: 12/08/2017 Number of Days to Update: 21 Source: Environmental Protection Agency Telephone: 202-564-8600 Last EDR Contact: 10/23/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Varies RAATS: RCRA Administrative Action Tracking System RCRA Administration Action Tracking System. RAATS contains records based on enforcement actions issued under RCRA pertaining to major violators and includes administrative and civil actions brought by the EPA. For administration actions after September 30, 1995, data entry in the RAATS database was discontinued. EPA will retain a copy of the database for historical records. It was necessary to terminate RAATS because a decrease in agency resources made it impossible to continue to update the information contained in the database. Date of Government Version: 04/17/1995 Date Data Arrived at EDR: 07/03/1995 Date Made Active in Reports: 08/07/1995 Number of Days to Update: 35 Source: EPA Telephone: 202-564-4104 Last EDR Contact: 06/02/2008 Next Scheduled EDR Contact: 09/01/2008 Data Release Frequency: No Update Planned TC5146125.2s Page GR-20 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING PRP: Potentially Responsible Parties A listing of verified Potentially Responsible Parties Date of Government Version: 10/25/2013 Date Data Arrived at EDR: 10/17/2014 Date Made Active in Reports: 10/20/2014 Number of Days to Update: 3 Source: EPA Telephone: 202-564-6023 Last EDR Contact: 12/22/2017 Next Scheduled EDR Contact: 02/19/2018 Data Release Frequency: Quarterly PADS: PCB Activity Database System PCB Activity Database. PADS Identifies generators, transporters, commercial storers and/or brokers and disposers of PCB’s who are required to notify the EPA of such activities. Date of Government Version: 06/01/2017 Date Data Arrived at EDR: 06/09/2017 Date Made Active in Reports: 10/13/2017 Number of Days to Update: 126 Source: EPA Telephone: 202-566-0500 Last EDR Contact: 10/13/2017 Next Scheduled EDR Contact: 01/22/2018 Data Release Frequency: Annually ICIS: Integrated Compliance Information System The Integrated Compliance Information System (ICIS) supports the information needs of the national enforcement and compliance program as well as the unique needs of the National Pollutant Discharge Elimination System (NPDES) program. Date of Government Version: 11/18/2016 Date Data Arrived at EDR: 11/23/2016 Date Made Active in Reports: 02/10/2017 Number of Days to Update: 79 Source: Environmental Protection Agency Telephone: 202-564-2501 Last EDR Contact: 10/11/2017 Next Scheduled EDR Contact: 01/22/2018 Data Release Frequency: Quarterly FTTS: FIFRA/ TSCA Tracking System - FIFRA (Federal Insecticide, Fungicide, & Rodenticide Act)/TSCA (Toxic Substances Control Act) FTTS tracks administrative cases and pesticide enforcement actions and compliance activities related to FIFRA, TSCA and EPCRA (Emergency Planning and Community Right-to-Know Act). To maintain currency, EDR contacts the Agency on a quarterly basis. Date of Government Version: 04/09/2009 Date Data Arrived at EDR: 04/16/2009 Date Made Active in Reports: 05/11/2009 Number of Days to Update: 25 Source: EPA/Office of Prevention, Pesticides and Toxic Substances Telephone: 202-566-1667 Last EDR Contact: 08/18/2017 Next Scheduled EDR Contact: 12/04/2017 Data Release Frequency: Quarterly FTTS INSP: FIFRA/ TSCA Tracking System - FIFRA (Federal Insecticide, Fungicide, & Rodenticide Act)/TSCA (Toxic Substances Control Act) A listing of FIFRA/TSCA Tracking System (FTTS) inspections and enforcements. Date of Government Version: 04/09/2009 Date Data Arrived at EDR: 04/16/2009 Date Made Active in Reports: 05/11/2009 Number of Days to Update: 25 Source: EPA Telephone: 202-566-1667 Last EDR Contact: 08/18/2017 Next Scheduled EDR Contact: 12/04/2017 Data Release Frequency: Quarterly MLTS: Material Licensing Tracking System MLTS is maintained by the Nuclear Regulatory Commission and contains a list of approximately 8,100 sites which possess or use radioactive materials and which are subject to NRC licensing requirements. To maintain currency, EDR contacts the Agency on a quarterly basis. Date of Government Version: 08/30/2016 Date Data Arrived at EDR: 09/08/2016 Date Made Active in Reports: 10/21/2016 Number of Days to Update: 43 Source: Nuclear Regulatory Commission Telephone: 301-415-7169 Last EDR Contact: 10/16/2017 Next Scheduled EDR Contact: 11/20/2017 Data Release Frequency: Quarterly TC5146125.2s Page GR-21 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING COAL ASH DOE: Steam-Electric Plant Operation Data A listing of power plants that store ash in surface ponds. Date of Government Version: 12/31/2005 Date Data Arrived at EDR: 08/07/2009 Date Made Active in Reports: 10/22/2009 Number of Days to Update: 76 Source: Department of Energy Telephone: 202-586-8719 Last EDR Contact: 12/05/2017 Next Scheduled EDR Contact: 03/19/2018 Data Release Frequency: Varies COAL ASH EPA: Coal Combustion Residues Surface Impoundments List A listing of coal combustion residues surface impoundments with high hazard potential ratings. Date of Government Version: 07/01/2014 Date Data Arrived at EDR: 09/10/2014 Date Made Active in Reports: 10/20/2014 Number of Days to Update: 40 Source: Environmental Protection Agency Telephone: N/A Last EDR Contact: 12/08/2017 Next Scheduled EDR Contact: 03/19/2018 Data Release Frequency: Varies PCB TRANSFORMER: PCB Transformer Registration Database The database of PCB transformer registrations that includes all PCB registration submittals. Date of Government Version: 05/24/2017 Date Data Arrived at EDR: 11/30/2017 Date Made Active in Reports: 12/15/2017 Number of Days to Update: 15 Source: Environmental Protection Agency Telephone: 202-566-0517 Last EDR Contact: 10/26/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Varies RADINFO: Radiation Information Database The Radiation Information Database (RADINFO) contains information about facilities that are regulated by U.S. Environmental Protection Agency (EPA) regulations for radiation and radioactivity. Date of Government Version: 10/02/2017 Date Data Arrived at EDR: 10/05/2017 Date Made Active in Reports: 10/13/2017 Number of Days to Update: 8 Source: Environmental Protection Agency Telephone: 202-343-9775 Last EDR Contact: 10/05/2017 Next Scheduled EDR Contact: 01/15/2018 Data Release Frequency: Quarterly HIST FTTS: FIFRA/TSCA Tracking System Administrative Case Listing A complete administrative case listing from the FIFRA/TSCA Tracking System (FTTS) for all ten EPA regions. The information was obtained from the National Compliance Database (NCDB). NCDB supports the implementation of FIFRA Federal Insecticide, Fungicide, and Rodenticide Act) and TSCA (Toxic Substances Control Act). Some EPA regions are now closing out records. Because of that, and the fact that some EPA regions are not providing EPA Headquarters with updated records, it was decided to create a HIST FTTS database. It included records that may not be included in the newer FTTS database updates. This database is no longer updated. Date of Government Version: 10/19/2006 Date Data Arrived at EDR: 03/01/2007 Date Made Active in Reports: 04/10/2007 Number of Days to Update: 40 Source: Environmental Protection Agency Telephone: 202-564-2501 Last EDR Contact: 12/17/2007 Next Scheduled EDR Contact: 03/17/2008 Data Release Frequency: No Update Planned HIST FTTS INSP: FIFRA/TSCA Tracking System Inspection & Enforcement Case Listing A complete inspection and enforcement case listing from the FIFRA/TSCA Tracking System (FTTS) for all ten EPA regions. The information was obtained from the National Compliance Database (NCDB). NCDB supports the implementation of FIFRA (Federal Insecticide, Fungicide, and Rodenticide Act) and TSCA (Toxic Substances Control Act). Some EPA regions are now closing out records. Because of that, and the fact that some EPA regions are not providing EPA Headquarters with updated records, it was decided to create a HIST FTTS database. It included records that may not be included in the newer FTTS database updates. This database is no longer updated. TC5146125.2s Page GR-22 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Date of Government Version: 10/19/2006 Date Data Arrived at EDR: 03/01/2007 Date Made Active in Reports: 04/10/2007 Number of Days to Update: 40 Source: Environmental Protection Agency Telephone: 202-564-2501 Last EDR Contact: 12/17/2008 Next Scheduled EDR Contact: 03/17/2008 Data Release Frequency: No Update Planned DOT OPS: Incident and Accident Data Department of Transporation, Office of Pipeline Safety Incident and Accident data. Date of Government Version: 07/31/2012 Date Data Arrived at EDR: 08/07/2012 Date Made Active in Reports: 09/18/2012 Number of Days to Update: 42 Source: Department of Transporation, Office of Pipeline Safety Telephone: 202-366-4595 Last EDR Contact: 10/31/2017 Next Scheduled EDR Contact: 02/12/2018 Data Release Frequency: Varies CONSENT: Superfund (CERCLA) Consent Decrees Major legal settlements that establish responsibility and standards for cleanup at NPL (Superfund) sites. Released periodically by United States District Courts after settlement by parties to litigation matters. Date of Government Version: 06/30/2017 Date Data Arrived at EDR: 08/03/2017 Date Made Active in Reports: 10/20/2017 Number of Days to Update: 78 Source: Department of Justice, Consent Decree Library Telephone: Varies Last EDR Contact: 12/18/2017 Next Scheduled EDR Contact: 04/02/2018 Data Release Frequency: Varies BRS: Biennial Reporting System The Biennial Reporting System is a national system administered by the EPA that collects data on the generation and management of hazardous waste. BRS captures detailed data from two groups: Large Quantity Generators (LQG) and Treatment, Storage, and Disposal Facilities. Date of Government Version: 12/31/2015 Date Data Arrived at EDR: 02/22/2017 Date Made Active in Reports: 09/28/2017 Number of Days to Update: 218 Source: EPA/NTIS Telephone: 800-424-9346 Last EDR Contact: 11/20/2017 Next Scheduled EDR Contact: 03/05/2018 Data Release Frequency: Biennially INDIAN RESERV: Indian Reservations This map layer portrays Indian administered lands of the United States that have any area equal to or greater than 640 acres. Date of Government Version: 12/31/2014 Date Data Arrived at EDR: 07/14/2015 Date Made Active in Reports: 01/10/2017 Number of Days to Update: 546 Source: USGS Telephone: 202-208-3710 Last EDR Contact: 10/11/2017 Next Scheduled EDR Contact: 01/22/2018 Data Release Frequency: Semi-Annually FUSRAP: Formerly Utilized Sites Remedial Action Program DOE established the Formerly Utilized Sites Remedial Action Program (FUSRAP) in 1974 to remediate sites where radioactive contamination remained from Manhattan Project and early U.S. Atomic Energy Commission (AEC) operations. Date of Government Version: 12/23/2016 Date Data Arrived at EDR: 12/27/2016 Date Made Active in Reports: 02/17/2017 Number of Days to Update: 52 Source: Department of Energy Telephone: 202-586-3559 Last EDR Contact: 11/02/2017 Next Scheduled EDR Contact: 02/19/2018 Data Release Frequency: Varies UMTRA: Uranium Mill Tailings Sites Uranium ore was mined by private companies for federal government use in national defense programs. When the mills shut down, large piles of the sand-like material (mill tailings) remain after uranium has been extracted from the ore. Levels of human exposure to radioactive materials from the piles are low; however, in some cases tailings were used as construction materials before the potential health hazards of the tailings were recognized. TC5146125.2s Page GR-23 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Date of Government Version: 06/23/2017 Date Data Arrived at EDR: 10/11/2017 Date Made Active in Reports: 11/03/2017 Number of Days to Update: 23 Source: Department of Energy Telephone: 505-845-0011 Last EDR Contact: 11/22/2017 Next Scheduled EDR Contact: 03/05/2018 Data Release Frequency: Varies LEAD SMELTER 1: Lead Smelter Sites A listing of former lead smelter site locations. Date of Government Version: 10/10/2017 Date Data Arrived at EDR: 11/03/2017 Date Made Active in Reports: 12/15/2017 Number of Days to Update: 42 Source: Environmental Protection Agency Telephone: 703-603-8787 Last EDR Contact: 12/22/2017 Next Scheduled EDR Contact: 01/15/2018 Data Release Frequency: Varies LEAD SMELTER 2: Lead Smelter Sites A list of several hundred sites in the U.S. where secondary lead smelting was done from 1931and 1964. These sites may pose a threat to public health through ingestion or inhalation of contaminated soil or dust Date of Government Version: 04/05/2001 Date Data Arrived at EDR: 10/27/2010 Date Made Active in Reports: 12/02/2010 Number of Days to Update: 36 Source: American Journal of Public Health Telephone: 703-305-6451 Last EDR Contact: 12/02/2009 Next Scheduled EDR Contact: N/A Data Release Frequency: No Update Planned US AIRS (AFS): Aerometric Information Retrieval System Facility Subsystem (AFS) The database is a sub-system of Aerometric Information Retrieval System (AIRS). AFS contains compliance data on air pollution point sources regulated by the U.S. EPA and/or state and local air regulatory agencies. This information comes from source reports by various stationary sources of air pollution, such as electric power plants, steel mills, factories, and universities, and provides information about the air pollutants they produce. Action, air program, air program pollutant, and general level plant data. It is used to track emissions and compliance data from industrial plants. Date of Government Version: 10/12/2016 Date Data Arrived at EDR: 10/26/2016 Date Made Active in Reports: 02/03/2017 Number of Days to Update: 100 Source: EPA Telephone: 202-564-2496 Last EDR Contact: 09/26/2017 Next Scheduled EDR Contact: 01/08/2018 Data Release Frequency: Annually US AIRS MINOR: Air Facility System Data A listing of minor source facilities. Date of Government Version: 10/12/2016 Date Data Arrived at EDR: 10/26/2016 Date Made Active in Reports: 02/03/2017 Number of Days to Update: 100 Source: EPA Telephone: 202-564-2496 Last EDR Contact: 09/26/2017 Next Scheduled EDR Contact: 01/08/2018 Data Release Frequency: Annually US MINES: Mines Master Index File Contains all mine identification numbers issued for mines active or opened since 1971. The data also includes violation information. Date of Government Version: 07/31/2017 Date Data Arrived at EDR: 08/30/2017 Date Made Active in Reports: 10/13/2017 Number of Days to Update: 44 Source: Department of Labor, Mine Safety and Health Administration Telephone: 303-231-5959 Last EDR Contact: 11/28/2017 Next Scheduled EDR Contact: 03/12/2018 Data Release Frequency: Semi-Annually US MINES 2: Ferrous and Nonferrous Metal Mines Database Listing This map layer includes ferrous (ferrous metal mines are facilities that extract ferrous metals, such as iron ore or molybdenum) and nonferrous (Nonferrous metal mines are facilities that extract nonferrous metals, such as gold, silver, copper, zinc, and lead) metal mines in the United States. TC5146125.2s Page GR-24 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Date of Government Version: 12/05/2005 Date Data Arrived at EDR: 02/29/2008 Date Made Active in Reports: 04/18/2008 Number of Days to Update: 49 Source: USGS Telephone: 703-648-7709 Last EDR Contact: 12/01/2017 Next Scheduled EDR Contact: 03/12/2018 Data Release Frequency: Varies US MINES 3: Active Mines & Mineral Plants Database Listing Active Mines and Mineral Processing Plant operations for commodities monitored by the Minerals Information Team of the USGS. Date of Government Version: 04/14/2011 Date Data Arrived at EDR: 06/08/2011 Date Made Active in Reports: 09/13/2011 Number of Days to Update: 97 Source: USGS Telephone: 703-648-7709 Last EDR Contact: 12/01/2017 Next Scheduled EDR Contact: 03/12/2018 Data Release Frequency: Varies ABANDONED MINES: Abandoned Mines An inventory of land and water impacted by past mining (primarily coal mining) is maintained by OSMRE to provide information needed to implement the Surface Mining Control and Reclamation Act of 1977 (SMCRA). The inventory contains information on the location, type, and extent of AML impacts, as well as, information on the cost associated with the reclamation of those problems. The inventory is based upon field surveys by State, Tribal, and OSMRE program officials. It is dynamic to the extent that it is modified as new problems are identified and existing problems are reclaimed. Date of Government Version: 09/25/2017 Date Data Arrived at EDR: 09/26/2017 Date Made Active in Reports: 10/20/2017 Number of Days to Update: 24 Source: Department of Interior Telephone: 202-208-2609 Last EDR Contact: 12/19/2017 Next Scheduled EDR Contact: 03/26/2018 Data Release Frequency: Quarterly FINDS: Facility Index System/Facility Registry System Facility Index System. FINDS contains both facility information and ’pointers’ to other sources that contain more detail. EDR includes the following FINDS databases in this report: PCS (Permit Compliance System), AIRS (Aerometric Information Retrieval System), DOCKET (Enforcement Docket used to manage and track information on civil judicial enforcement cases for all environmental statutes), FURS (Federal Underground Injection Control), C-DOCKET (Criminal Docket System used to track criminal enforcement actions for all environmental statutes), FFIS (Federal Facilities Information System), STATE (State Environmental Laws and Statutes), and PADS (PCB Activity Data System). Date of Government Version: 07/23/2017 Date Data Arrived at EDR: 09/06/2017 Date Made Active in Reports: 09/15/2017 Number of Days to Update: 9 Source: EPA Telephone: (415) 947-8000 Last EDR Contact: 12/05/2017 Next Scheduled EDR Contact: 03/19/2018 Data Release Frequency: Quarterly ECHO: Enforcement & Compliance History Information ECHO provides integrated compliance and enforcement information for about 800,000 regulated facilities nationwide. Date of Government Version: 09/02/2017 Date Data Arrived at EDR: 09/06/2017 Date Made Active in Reports: 10/20/2017 Number of Days to Update: 44 Source: Environmental Protection Agency Telephone: 202-564-2280 Last EDR Contact: 12/05/2017 Next Scheduled EDR Contact: 03/19/2018 Data Release Frequency: Quarterly DOCKET HWC: Hazardous Waste Compliance Docket Listing A complete list of the Federal Agency Hazardous Waste Compliance Docket Facilities. Date of Government Version: 02/13/2017 Date Data Arrived at EDR: 02/15/2017 Date Made Active in Reports: 11/03/2017 Number of Days to Update: 261 Source: Environmental Protection Agency Telephone: 202-564-0527 Last EDR Contact: 11/21/2017 Next Scheduled EDR Contact: 03/12/2018 Data Release Frequency: Varies TC5146125.2s Page GR-25 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING UXO: Unexploded Ordnance Sites A listing of unexploded ordnance site locations Date of Government Version: 10/25/2016 Date Data Arrived at EDR: 06/02/2017 Date Made Active in Reports: 10/13/2017 Number of Days to Update: 133 Source: Department of Defense Telephone: 703-704-1564 Last EDR Contact: 10/16/2017 Next Scheduled EDR Contact: 01/29/2018 Data Release Frequency: Varies FUELS PROGRAM: EPA Fuels Program Registered Listing This listing includes facilities that are registered under the Part 80 (Code of Federal Regulations) EPA Fuels Programs. All companies now are required to submit new and updated registrations. Date of Government Version: 08/17/2017 Date Data Arrived at EDR: 08/17/2017 Date Made Active in Reports: 09/15/2017 Number of Days to Update: 29 Source: EPA Telephone: 800-385-6164 Last EDR Contact: 11/20/2017 Next Scheduled EDR Contact: 03/05/2018 Data Release Frequency: Quarterly CA BOND EXP. PLAN: Bond Expenditure Plan Department of Health Services developed a site-specific expenditure plan as the basis for an appropriation of Hazardous Substance Cleanup Bond Act funds. It is not updated. Date of Government Version: 01/01/1989 Date Data Arrived at EDR: 07/27/1994 Date Made Active in Reports: 08/02/1994 Number of Days to Update: 6 Source: Department of Health Services Telephone: 916-255-2118 Last EDR Contact: 05/31/1994 Next Scheduled EDR Contact: N/A Data Release Frequency: No Update Planned CORTESE: "Cortese" Hazardous Waste & Substances Sites List The sites for the list are designated by the State Water Resource Control Board (LUST), the Integrated Waste Board (SWF/LS), and the Department of Toxic Substances Control (Cal-Sites). Date of Government Version: 09/21/2017 Date Data Arrived at EDR: 09/21/2017 Date Made Active in Reports: 10/13/2017 Number of Days to Update: 22 Source: CAL EPA/Office of Emergency Information Telephone: 916-323-3400 Last EDR Contact: 09/21/2017 Next Scheduled EDR Contact: 01/01/2018 Data Release Frequency: Quarterly DRYCLEANERS: Cleaner Facilities A list of drycleaner related facilities that have EPA ID numbers. These are facilities with certain SIC codes: power laundries, family and commercial; garment pressing and cleaner’s agents; linen supply; coin-operated laundries and cleaning; drycleaning plants, except rugs; carpet and upholster cleaning; industrial launderers; laundry and garment services. Date of Government Version: 08/02/2017 Date Data Arrived at EDR: 08/08/2017 Date Made Active in Reports: 10/16/2017 Number of Days to Update: 69 Source: Department of Toxic Substance Control Telephone: 916-327-4498 Last EDR Contact: 11/30/2017 Next Scheduled EDR Contact: 03/19/2018 Data Release Frequency: Annually EMI: Emissions Inventory Data Toxics and criteria pollutant emissions data collected by the ARB and local air pollution agencies. Date of Government Version: 12/31/2015 Date Data Arrived at EDR: 03/21/2017 Date Made Active in Reports: 08/15/2017 Number of Days to Update: 147 Source: California Air Resources Board Telephone: 916-322-2990 Last EDR Contact: 12/22/2017 Next Scheduled EDR Contact: 04/02/2018 Data Release Frequency: Varies TC5146125.2s Page GR-26 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING ENF: Enforcement Action Listing A listing of Water Board Enforcement Actions. Formal is everything except Oral/Verbal Communication, Notice of Violation, Expedited Payment Letter, and Staff Enforcement Letter. Date of Government Version: 11/01/2017 Date Data Arrived at EDR: 11/03/2017 Date Made Active in Reports: 12/07/2017 Number of Days to Update: 34 Source: State Water Resoruces Control Board Telephone: 916-445-9379 Last EDR Contact: 11/01/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Varies Financial Assurance 1: Financial Assurance Information Listing Financial Assurance information Date of Government Version: 10/23/2017 Date Data Arrived at EDR: 10/24/2017 Date Made Active in Reports: 12/15/2017 Number of Days to Update: 52 Source: Department of Toxic Substances Control Telephone: 916-255-3628 Last EDR Contact: 10/23/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Varies Financial Assurance 2: Financial Assurance Information Listing A listing of financial assurance information for solid waste facilities. Financial assurance is intended to ensure that resources are available to pay for the cost of closure, post-closure care, and corrective measures if the owner or operator of a regulated facility is unable or unwilling to pay. Date of Government Version: 11/14/2017 Date Data Arrived at EDR: 11/17/2017 Date Made Active in Reports: 12/18/2017 Number of Days to Update: 31 Source: California Integrated Waste Management Board Telephone: 916-341-6066 Last EDR Contact: 11/09/2017 Next Scheduled EDR Contact: 02/26/2018 Data Release Frequency: Varies HAZNET: Facility and Manifest Data Facility and Manifest Data. The data is extracted from the copies of hazardous waste manifests received each year by the DTSC. The annual volume of manifests is typically 700,000 - 1,000,000 annually, representing approximately 350,000 - 500,000 shipments. Data are from the manifests submitted without correction, and therefore many contain some invalid values for data elements such as generator ID, TSD ID, waste category, and disposal method. This database begins with calendar year 1993. Date of Government Version: 12/31/2016 Date Data Arrived at EDR: 07/12/2017 Date Made Active in Reports: 10/17/2017 Number of Days to Update: 97 Source: California Environmental Protection Agency Telephone: 916-255-1136 Last EDR Contact: 10/10/2017 Next Scheduled EDR Contact: 01/22/2018 Data Release Frequency: Annually ICE: ICE Contains data pertaining to the Permitted Facilities with Inspections / Enforcements sites tracked in Envirostor. Date of Government Version: 08/21/2017 Date Data Arrived at EDR: 08/22/2017 Date Made Active in Reports: 10/25/2017 Number of Days to Update: 64 Source: Department of Toxic Subsances Control Telephone: 877-786-9427 Last EDR Contact: 11/20/2017 Next Scheduled EDR Contact: 03/05/2018 Data Release Frequency: Quarterly HIST CORTESE: Hazardous Waste & Substance Site List The sites for the list are designated by the State Water Resource Control Board [LUST], the Integrated Waste Board SWF/LS], and the Department of Toxic Substances Control [CALSITES]. This listing is no longer updated by the state agency. Date of Government Version: 04/01/2001 Date Data Arrived at EDR: 01/22/2009 Date Made Active in Reports: 04/08/2009 Number of Days to Update: 76 Source: Department of Toxic Substances Control Telephone: 916-323-3400 Last EDR Contact: 01/22/2009 Next Scheduled EDR Contact: N/A Data Release Frequency: No Update Planned TC5146125.2s Page GR-27 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING HWP: EnviroStor Permitted Facilities Listing Detailed information on permitted hazardous waste facilities and corrective action ("cleanups") tracked in EnviroStor. Date of Government Version: 08/21/2017 Date Data Arrived at EDR: 08/22/2017 Date Made Active in Reports: 10/25/2017 Number of Days to Update: 64 Source: Department of Toxic Substances Control Telephone: 916-323-3400 Last EDR Contact: 11/20/2017 Next Scheduled EDR Contact: 03/05/2018 Data Release Frequency: Quarterly HWT: Registered Hazardous Waste Transporter Database A listing of hazardous waste transporters. In California, unless specifically exempted, it is unlawful for any person to transport hazardous wastes unless the person holds a valid registration issued by DTSC. A hazardous waste transporter registration is valid for one year and is assigned a unique registration number. Date of Government Version: 10/10/2017 Date Data Arrived at EDR: 10/10/2017 Date Made Active in Reports: 10/17/2017 Number of Days to Update: 7 Source: Department of Toxic Substances Control Telephone: 916-440-7145 Last EDR Contact: 10/10/2017 Next Scheduled EDR Contact: 01/22/2018 Data Release Frequency: Quarterly MINES: Mines Site Location Listing A listing of mine site locations from the Office of Mine Reclamation. Date of Government Version: 09/11/2017 Date Data Arrived at EDR: 09/12/2017 Date Made Active in Reports: 11/01/2017 Number of Days to Update: 50 Source: Department of Conservation Telephone: 916-322-1080 Last EDR Contact: 12/12/2017 Next Scheduled EDR Contact: 03/26/2018 Data Release Frequency: Quarterly MWMP: Medical Waste Management Program Listing The Medical Waste Management Program (MWMP) ensures the proper handling and disposal of medical waste by permitting and inspecting medical waste Offsite Treatment Facilities (PDF) and Transfer Stations (PDF) throughout the state. MWMP also oversees all Medical Waste Transporters. Date of Government Version: 09/01/2017 Date Data Arrived at EDR: 09/06/2017 Date Made Active in Reports: 11/08/2017 Number of Days to Update: 63 Source: Department of Public Health Telephone: 916-558-1784 Last EDR Contact: 12/05/2017 Next Scheduled EDR Contact: 03/19/2018 Data Release Frequency: Varies NPDES: NPDES Permits Listing A listing of NPDES permits, including stormwater. Date of Government Version: 11/13/2017 Date Data Arrived at EDR: 11/14/2017 Date Made Active in Reports: 12/07/2017 Number of Days to Update: 23 Source: State Water Resources Control Board Telephone: 916-445-9379 Last EDR Contact: 11/14/2017 Next Scheduled EDR Contact: 02/26/2018 Data Release Frequency: Quarterly PEST LIC: Pesticide Regulation Licenses Listing A listing of licenses and certificates issued by the Department of Pesticide Regulation. The DPR issues licenses and/or certificates to: Persons and businesses that apply or sell pesticides; Pest control dealers and brokers; Persons who advise on agricultural pesticide applications. Date of Government Version: 09/05/2017 Date Data Arrived at EDR: 09/06/2017 Date Made Active in Reports: 11/08/2017 Number of Days to Update: 63 Source: Department of Pesticide Regulation Telephone: 916-445-4038 Last EDR Contact: 12/05/2017 Next Scheduled EDR Contact: 03/19/2018 Data Release Frequency: Quarterly TC5146125.2s Page GR-28 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING PROC: Certified Processors Database A listing of certified processors. Date of Government Version: 09/11/2017 Date Data Arrived at EDR: 09/12/2017 Date Made Active in Reports: 10/18/2017 Number of Days to Update: 36 Source: Department of Conservation Telephone: 916-323-3836 Last EDR Contact: 12/12/2017 Next Scheduled EDR Contact: 03/26/2018 Data Release Frequency: Quarterly NOTIFY 65: Proposition 65 Records Listings of all Proposition 65 incidents reported to counties by the State Water Resources Control Board and the Regional Water Quality Control Board. This database is no longer updated by the reporting agency. Date of Government Version: 06/16/2017 Date Data Arrived at EDR: 06/20/2017 Date Made Active in Reports: 10/17/2017 Number of Days to Update: 119 Source: State Water Resources Control Board Telephone: 916-445-3846 Last EDR Contact: 12/13/2017 Next Scheduled EDR Contact: 04/02/2018 Data Release Frequency: No Update Planned UIC: UIC Listing A listing of wells identified as underground injection wells, in the California Oil and Gas Wells database. Date of Government Version: 09/11/2017 Date Data Arrived at EDR: 09/12/2017 Date Made Active in Reports: 12/15/2017 Number of Days to Update: 94 Source: Deaprtment of Conservation Telephone: 916-445-2408 Last EDR Contact: 12/12/2017 Next Scheduled EDR Contact: 03/26/2018 Data Release Frequency: Varies WASTEWATER PITS: Oil Wastewater Pits Listing Water officials discovered that oil producers have been dumping chemical-laden wastewater into hundreds of unlined pits that are operating without proper permits. Inspections completed by the Central Valley Regional Water Quality Control Board revealed the existence of previously unidentified waste sites. The water board?s review found that more than one-third of the region?s active disposal pits are operating without permission. Date of Government Version: 04/15/2015 Date Data Arrived at EDR: 04/17/2015 Date Made Active in Reports: 06/23/2015 Number of Days to Update: 67 Source: RWQCB, Central Valley Region Telephone: 559-445-5577 Last EDR Contact: 10/13/2017 Next Scheduled EDR Contact: 01/22/2018 Data Release Frequency: Varies WDS: Waste Discharge System Sites which have been issued waste discharge requirements. Date of Government Version: 06/19/2007 Date Data Arrived at EDR: 06/20/2007 Date Made Active in Reports: 06/29/2007 Number of Days to Update: 9 Source: State Water Resources Control Board Telephone: 916-341-5227 Last EDR Contact: 11/14/2017 Next Scheduled EDR Contact: 03/05/2018 Data Release Frequency: Quarterly WIP: Well Investigation Program Case List Well Investigation Program case in the San Gabriel and San Fernando Valley area. Date of Government Version: 07/03/2009 Date Data Arrived at EDR: 07/21/2009 Date Made Active in Reports: 08/03/2009 Number of Days to Update: 13 Source: Los Angeles Water Quality Control Board Telephone: 213-576-6726 Last EDR Contact: 12/19/2017 Next Scheduled EDR Contact: 04/09/2018 Data Release Frequency: Varies TC5146125.2s Page GR-29 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING EDR HIGH RISK HISTORICAL RECORDS EDR Exclusive Records EDR MGP: EDR Proprietary Manufactured Gas Plants The EDR Proprietary Manufactured Gas Plant Database includes records of coal gas plants (manufactured gas plants) compiled by EDR’s researchers. Manufactured gas sites were used in the United States from the 1800’s to 1950’s to produce a gas that could be distributed and used as fuel. These plants used whale oil, rosin, coal, or a mixture of coal, oil, and water that also produced a significant amount of waste. Many of the byproducts of the gas production, such as coal tar (oily waste containing volatile and non-volatile chemicals), sludges, oils and other compounds are potentially hazardous to human health and the environment. The byproduct from this process was frequently disposed of directly at the plant site and can remain or spread slowly, serving as a continuous source of soil and groundwater contamination. Date of Government Version: N/A Date Data Arrived at EDR: N/A Date Made Active in Reports: N/A Number of Days to Update: N/A Source: EDR, Inc. Telephone: N/A Last EDR Contact: N/A Next Scheduled EDR Contact: N/A Data Release Frequency: No Update Planned EDR Hist Auto: EDR Exclusive Historical Auto Stations EDR has searched selected national collections of business directories and has collected listings of potential gas station/filling station/service station sites that were available to EDR researchers. EDR’s review was limited to those categories of sources that might, in EDR’s opinion, include gas station/filling station/service station establishments. The categories reviewed included, but were not limited to gas, gas station, gasoline station, filling station, auto, automobile repair, auto service station, service station, etc. This database falls within a category of information EDR classifies as "High Risk Historical Records", or HRHR. EDR’s HRHR effort presents unique and sometimes proprietary data about past sites and operations that typically create environmental concerns, but may not show up in current government records searches. Date of Government Version: N/A Date Data Arrived at EDR: N/A Date Made Active in Reports: N/A Number of Days to Update: N/A Source: EDR, Inc. Telephone: N/A Last EDR Contact: N/A Next Scheduled EDR Contact: N/A Data Release Frequency: Varies EDR Hist Cleaner: EDR Exclusive Historical Cleaners EDR has searched selected national collections of business directories and has collected listings of potential dry cleaner sites that were available to EDR researchers. EDR’s review was limited to those categories of sources that might, in EDR’s opinion, include dry cleaning establishments. The categories reviewed included, but were not limited to dry cleaners, cleaners, laundry, laundromat, cleaning/laundry, wash & dry etc. This database falls within a category of information EDR classifies as "High Risk Historical Records", or HRHR. EDR’s HRHR effort presents unique and sometimes proprietary data about past sites and operations that typically create environmental concerns, but may not show up in current government records searches. Date of Government Version: N/A Date Data Arrived at EDR: N/A Date Made Active in Reports: N/A Number of Days to Update: N/A Source: EDR, Inc. Telephone: N/A Last EDR Contact: N/A Next Scheduled EDR Contact: N/A Data Release Frequency: Varies EDR RECOVERED GOVERNMENT ARCHIVES Exclusive Recovered Govt. Archives RGA LF: Recovered Government Archive Solid Waste Facilities List The EDR Recovered Government Archive Landfill database provides a list of landfills derived from historical databases and includes many records that no longer appear in current government lists. Compiled from Records formerly available from the Department of Resources Recycling and Recovery in California. TC5146125.2s Page GR-30 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Date of Government Version: N/A Date Data Arrived at EDR: 07/01/2013 Date Made Active in Reports: 01/13/2014 Number of Days to Update: 196 Source: Department of Resources Recycling and Recovery Telephone: N/A Last EDR Contact: 06/01/2012 Next Scheduled EDR Contact: N/A Data Release Frequency: Varies RGA LUST: Recovered Government Archive Leaking Underground Storage Tank The EDR Recovered Government Archive Leaking Underground Storage Tank database provides a list of LUST incidents derived from historical databases and includes many records that no longer appear in current government lists. Compiled from Records formerly available from the State Water Resources Control Board in California. Date of Government Version: N/A Date Data Arrived at EDR: 07/01/2013 Date Made Active in Reports: 12/30/2013 Number of Days to Update: 182 Source: State Water Resources Control Board Telephone: N/A Last EDR Contact: 06/01/2012 Next Scheduled EDR Contact: N/A Data Release Frequency: Varies COUNTY RECORDS ALAMEDA COUNTY: Contaminated Sites A listing of contaminated sites overseen by the Toxic Release Program (oil and groundwater contamination from chemical releases and spills) and the Leaking Underground Storage Tank Program (soil and ground water contamination from leaking petroleum USTs). Date of Government Version: 09/22/2017 Date Data Arrived at EDR: 09/22/2017 Date Made Active in Reports: 10/10/2017 Number of Days to Update: 18 Source: Alameda County Environmental Health Services Telephone: 510-567-6700 Last EDR Contact: 09/21/2017 Next Scheduled EDR Contact: 01/22/2018 Data Release Frequency: Semi-Annually Underground Tanks Underground storage tank sites located in Alameda county. Date of Government Version: 10/11/2017 Date Data Arrived at EDR: 10/12/2017 Date Made Active in Reports: 11/08/2017 Number of Days to Update: 27 Source: Alameda County Environmental Health Services Telephone: 510-567-6700 Last EDR Contact: 10/10/2017 Next Scheduled EDR Contact: 04/24/2047 Data Release Frequency: Semi-Annually AMADOR COUNTY: CUPA Facility List Cupa Facility List Date of Government Version: 09/13/2017 Date Data Arrived at EDR: 09/15/2017 Date Made Active in Reports: 11/14/2017 Number of Days to Update: 60 Source: Amador County Environmental Health Telephone: 209-223-6439 Last EDR Contact: 11/30/2017 Next Scheduled EDR Contact: 03/19/2018 Data Release Frequency: Varies BUTTE COUNTY: CUPA Facility Listing Cupa facility list. TC5146125.2s Page GR-31 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Date of Government Version: 04/21/2017 Date Data Arrived at EDR: 04/25/2017 Date Made Active in Reports: 08/09/2017 Number of Days to Update: 106 Source: Public Health Department Telephone: 530-538-7149 Last EDR Contact: 09/18/2017 Next Scheduled EDR Contact: 10/23/2017 Data Release Frequency: No Update Planned CALVERAS COUNTY: CUPA Facility Listing Cupa Facility Listing Date of Government Version: 08/31/2017 Date Data Arrived at EDR: 09/05/2017 Date Made Active in Reports: 11/08/2017 Number of Days to Update: 64 Source: Calveras County Environmental Health Telephone: 209-754-6399 Last EDR Contact: 12/20/2017 Next Scheduled EDR Contact: 10/09/2017 Data Release Frequency: Quarterly COLUSA COUNTY: CUPA Facility List Cupa facility list. Date of Government Version: 08/07/2017 Date Data Arrived at EDR: 08/08/2017 Date Made Active in Reports: 10/16/2017 Number of Days to Update: 69 Source: Health & Human Services Telephone: 530-458-0396 Last EDR Contact: 11/01/2017 Next Scheduled EDR Contact: 02/19/2018 Data Release Frequency: Semi-Annually CONTRA COSTA COUNTY: Site List List includes sites from the underground tank, hazardous waste generator and business plan/2185 programs. Date of Government Version: 08/17/2017 Date Data Arrived at EDR: 08/22/2017 Date Made Active in Reports: 10/25/2017 Number of Days to Update: 64 Source: Contra Costa Health Services Department Telephone: 925-646-2286 Last EDR Contact: 10/30/2017 Next Scheduled EDR Contact: 02/12/2018 Data Release Frequency: Semi-Annually DEL NORTE COUNTY: CUPA Facility List Cupa Facility list Date of Government Version: 10/31/2017 Date Data Arrived at EDR: 11/01/2017 Date Made Active in Reports: 11/14/2017 Number of Days to Update: 13 Source: Del Norte County Environmental Health Division Telephone: 707-465-0426 Last EDR Contact: 10/25/2017 Next Scheduled EDR Contact: 02/12/2018 Data Release Frequency: Varies EL DORADO COUNTY: CUPA Facility List CUPA facility list. TC5146125.2s Page GR-32 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Date of Government Version: 08/18/2017 Date Data Arrived at EDR: 08/22/2017 Date Made Active in Reports: 10/24/2017 Number of Days to Update: 63 Source: El Dorado County Environmental Management Department Telephone: 530-621-6623 Last EDR Contact: 10/30/2017 Next Scheduled EDR Contact: 02/12/2018 Data Release Frequency: Varies FRESNO COUNTY: CUPA Resources List Certified Unified Program Agency. CUPA’s are responsible for implementing a unified hazardous materials and hazardous waste management regulatory program. The agency provides oversight of businesses that deal with hazardous materials, operate underground storage tanks or aboveground storage tanks. Date of Government Version: 10/03/2017 Date Data Arrived at EDR: 10/06/2017 Date Made Active in Reports: 11/15/2017 Number of Days to Update: 40 Source: Dept. of Community Health Telephone: 559-445-3271 Last EDR Contact: 09/27/2017 Next Scheduled EDR Contact: 01/15/2018 Data Release Frequency: Semi-Annually GLENN COUNTY: CUPA Facility List Cupa facility list Date of Government Version: 10/25/2017 Date Data Arrived at EDR: 10/27/2017 Date Made Active in Reports: 11/15/2017 Number of Days to Update: 19 Source: Glenn County Air Pollution Control District Telephone: 830-934-6500 Last EDR Contact: 10/23/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Varies HUMBOLDT COUNTY: CUPA Facility List CUPA facility list. Date of Government Version: 08/03/2017 Date Data Arrived at EDR: 08/08/2017 Date Made Active in Reports: 10/16/2017 Number of Days to Update: 69 Source: Humboldt County Environmental Health Telephone: N/A Last EDR Contact: 11/14/2017 Next Scheduled EDR Contact: 03/05/2018 Data Release Frequency: Semi-Annually IMPERIAL COUNTY: CUPA Facility List Cupa facility list. Date of Government Version: 10/23/2017 Date Data Arrived at EDR: 10/24/2017 Date Made Active in Reports: 11/15/2017 Number of Days to Update: 22 Source: San Diego Border Field Office Telephone: 760-339-2777 Last EDR Contact: 10/23/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Varies INYO COUNTY: TC5146125.2s Page GR-33 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING CUPA Facility List Cupa facility list. Date of Government Version: 06/08/2017 Date Data Arrived at EDR: 06/09/2017 Date Made Active in Reports: 08/04/2017 Number of Days to Update: 56 Source: Inyo County Environmental Health Services Telephone: 760-878-0238 Last EDR Contact: 11/14/2017 Next Scheduled EDR Contact: 03/05/2018 Data Release Frequency: Varies KERN COUNTY: Underground Storage Tank Sites & Tank Listing Kern County Sites and Tanks Listing. Date of Government Version: 11/02/2017 Date Data Arrived at EDR: 11/07/2017 Date Made Active in Reports: 12/20/2017 Number of Days to Update: 43 Source: Kern County Environment Health Services Department Telephone: 661-862-8700 Last EDR Contact: 11/01/2017 Next Scheduled EDR Contact: 02/19/2018 Data Release Frequency: Quarterly KINGS COUNTY: CUPA Facility List A listing of sites included in the county’s Certified Unified Program Agency database. California’s Secretary for Environmental Protection established the unified hazardous materials and hazardous waste regulatory program as required by chapter 6.11 of the California Health and Safety Code. The Unified Program consolidates the administration, permits, inspections, and enforcement activities. Date of Government Version: 11/14/2017 Date Data Arrived at EDR: 11/17/2017 Date Made Active in Reports: 12/15/2017 Number of Days to Update: 28 Source: Kings County Department of Public Health Telephone: 559-584-1411 Last EDR Contact: 11/14/2017 Next Scheduled EDR Contact: 03/05/2018 Data Release Frequency: Varies LAKE COUNTY: CUPA Facility List Cupa facility list Date of Government Version: 11/09/2017 Date Data Arrived at EDR: 11/10/2017 Date Made Active in Reports: 11/15/2017 Number of Days to Update: 5 Source: Lake County Environmental Health Telephone: 707-263-1164 Last EDR Contact: 10/16/2017 Next Scheduled EDR Contact: 01/29/2018 Data Release Frequency: Varies LASSEN COUNTY: CUPA Facility List Cupa facility list Date of Government Version: 07/24/2017 Date Data Arrived at EDR: 07/26/2017 Date Made Active in Reports: 10/16/2017 Number of Days to Update: 82 Source: Lassen County Environmental Health Telephone: 530-251-8528 Last EDR Contact: 10/23/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Varies LOS ANGELES COUNTY: TC5146125.2s Page GR-34 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING San Gabriel Valley Areas of Concern San Gabriel Valley areas where VOC contamination is at or above the MCL as designated by region 9 EPA office. Date of Government Version: 03/30/2009 Date Data Arrived at EDR: 03/31/2009 Date Made Active in Reports: 10/23/2009 Number of Days to Update: 206 Source: EPA Region 9 Telephone: 415-972-3178 Last EDR Contact: 12/13/2017 Next Scheduled EDR Contact: 04/02/2018 Data Release Frequency: No Update Planned HMS: Street Number List Industrial Waste and Underground Storage Tank Sites. Date of Government Version: 10/11/2017 Date Data Arrived at EDR: 10/12/2017 Date Made Active in Reports: 10/17/2017 Number of Days to Update: 5 Source: Department of Public Works Telephone: 626-458-3517 Last EDR Contact: 10/10/2017 Next Scheduled EDR Contact: 01/22/2018 Data Release Frequency: Semi-Annually List of Solid Waste Facilities Solid Waste Facilities in Los Angeles County. Date of Government Version: 10/16/2017 Date Data Arrived at EDR: 10/17/2017 Date Made Active in Reports: 12/07/2017 Number of Days to Update: 51 Source: La County Department of Public Works Telephone: 818-458-5185 Last EDR Contact: 10/17/2017 Next Scheduled EDR Contact: 01/29/2018 Data Release Frequency: Varies City of Los Angeles Landfills Landfills owned and maintained by the City of Los Angeles. Date of Government Version: 01/01/2017 Date Data Arrived at EDR: 04/21/2017 Date Made Active in Reports: 10/09/2017 Number of Days to Update: 171 Source: Engineering & Construction Division Telephone: 213-473-7869 Last EDR Contact: 10/16/2017 Next Scheduled EDR Contact: 01/29/2018 Data Release Frequency: Varies Site Mitigation List Industrial sites that have had some sort of spill or complaint. Date of Government Version: 11/01/2017 Date Data Arrived at EDR: 11/14/2017 Date Made Active in Reports: 12/15/2017 Number of Days to Update: 31 Source: Community Health Services Telephone: 323-890-7806 Last EDR Contact: 11/14/2017 Next Scheduled EDR Contact: 01/29/2018 Data Release Frequency: Annually City of El Segundo Underground Storage Tank Underground storage tank sites located in El Segundo city. Date of Government Version: 01/21/2017 Date Data Arrived at EDR: 04/19/2017 Date Made Active in Reports: 05/10/2017 Number of Days to Update: 21 Source: City of El Segundo Fire Department Telephone: 310-524-2236 Last EDR Contact: 10/16/2017 Next Scheduled EDR Contact: 01/29/2018 Data Release Frequency: Semi-Annually City of Long Beach Underground Storage Tank Underground storage tank sites located in the city of Long Beach. Date of Government Version: 03/09/2017 Date Data Arrived at EDR: 03/10/2017 Date Made Active in Reports: 05/03/2017 Number of Days to Update: 54 Source: City of Long Beach Fire Department Telephone: 562-570-2563 Last EDR Contact: 10/23/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Annually TC5146125.2s Page GR-35 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING City of Torrance Underground Storage Tank Underground storage tank sites located in the city of Torrance. Date of Government Version: 07/11/2017 Date Data Arrived at EDR: 07/14/2017 Date Made Active in Reports: 09/21/2017 Number of Days to Update: 69 Source: City of Torrance Fire Department Telephone: 310-618-2973 Last EDR Contact: 10/10/2017 Next Scheduled EDR Contact: 01/22/2018 Data Release Frequency: Semi-Annually MADERA COUNTY: CUPA Facility List A listing of sites included in the county’s Certified Unified Program Agency database. California’s Secretary for Environmental Protection established the unified hazardous materials and hazardous waste regulatory program as required by chapter 6.11 of the California Health and Safety Code. The Unified Program consolidates the administration, permits, inspections, and enforcement activities. Date of Government Version: 10/26/2017 Date Data Arrived at EDR: 10/27/2017 Date Made Active in Reports: 11/06/2017 Number of Days to Update: 10 Source: Madera County Environmental Health Telephone: 559-675-7823 Last EDR Contact: 11/14/2017 Next Scheduled EDR Contact: 03/05/2018 Data Release Frequency: Varies MARIN COUNTY: Underground Storage Tank Sites Currently permitted USTs in Marin County. Date of Government Version: 09/28/2017 Date Data Arrived at EDR: 10/05/2017 Date Made Active in Reports: 11/08/2017 Number of Days to Update: 34 Source: Public Works Department Waste Management Telephone: 415-473-6647 Last EDR Contact: 09/27/2017 Next Scheduled EDR Contact: 01/15/2018 Data Release Frequency: Semi-Annually MERCED COUNTY: CUPA Facility List CUPA facility list. Date of Government Version: 10/02/2017 Date Data Arrived at EDR: 10/03/2017 Date Made Active in Reports: 10/17/2017 Number of Days to Update: 14 Source: Merced County Environmental Health Telephone: 209-381-1094 Last EDR Contact: 11/30/2017 Next Scheduled EDR Contact: 03/05/2018 Data Release Frequency: Varies MONO COUNTY: CUPA Facility List CUPA Facility List Date of Government Version: 08/08/2017 Date Data Arrived at EDR: 09/06/2017 Date Made Active in Reports: 10/16/2017 Number of Days to Update: 40 Source: Mono County Health Department Telephone: 760-932-5580 Last EDR Contact: 11/21/2017 Next Scheduled EDR Contact: 03/12/2018 Data Release Frequency: Varies MONTEREY COUNTY: TC5146125.2s Page GR-36 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING CUPA Facility Listing CUPA Program listing from the Environmental Health Division. Date of Government Version: 09/11/2017 Date Data Arrived at EDR: 09/15/2017 Date Made Active in Reports: 11/28/2017 Number of Days to Update: 74 Source: Monterey County Health Department Telephone: 831-796-1297 Last EDR Contact: 11/20/2017 Next Scheduled EDR Contact: 03/05/2018 Data Release Frequency: Varies NAPA COUNTY: Sites With Reported Contamination A listing of leaking underground storage tank sites located in Napa county. Date of Government Version: 01/09/2017 Date Data Arrived at EDR: 01/11/2017 Date Made Active in Reports: 03/02/2017 Number of Days to Update: 50 Source: Napa County Department of Environmental Management Telephone: 707-253-4269 Last EDR Contact: 11/21/2017 Next Scheduled EDR Contact: 03/12/2018 Data Release Frequency: No Update Planned Closed and Operating Underground Storage Tank Sites Underground storage tank sites located in Napa county. Date of Government Version: 11/22/2017 Date Data Arrived at EDR: 11/27/2017 Date Made Active in Reports: 12/19/2017 Number of Days to Update: 22 Source: Napa County Department of Environmental Management Telephone: 707-253-4269 Last EDR Contact: 11/21/2017 Next Scheduled EDR Contact: 03/12/2018 Data Release Frequency: No Update Planned NEVADA COUNTY: CUPA Facility List CUPA facility list. Date of Government Version: 11/02/2017 Date Data Arrived at EDR: 11/07/2017 Date Made Active in Reports: 11/15/2017 Number of Days to Update: 8 Source: Community Development Agency Telephone: 530-265-1467 Last EDR Contact: 10/25/2017 Next Scheduled EDR Contact: 02/12/2018 Data Release Frequency: Varies ORANGE COUNTY: List of Industrial Site Cleanups Petroleum and non-petroleum spills. Date of Government Version: 11/02/2017 Date Data Arrived at EDR: 11/09/2017 Date Made Active in Reports: 12/07/2017 Number of Days to Update: 28 Source: Health Care Agency Telephone: 714-834-3446 Last EDR Contact: 11/06/2017 Next Scheduled EDR Contact: 02/19/2018 Data Release Frequency: Annually List of Underground Storage Tank Cleanups Orange County Underground Storage Tank Cleanups (LUST). Date of Government Version: 11/02/2017 Date Data Arrived at EDR: 11/09/2017 Date Made Active in Reports: 12/15/2017 Number of Days to Update: 36 Source: Health Care Agency Telephone: 714-834-3446 Last EDR Contact: 11/06/2017 Next Scheduled EDR Contact: 02/19/2018 Data Release Frequency: Quarterly TC5146125.2s Page GR-37 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING List of Underground Storage Tank Facilities Orange County Underground Storage Tank Facilities (UST). Date of Government Version: 11/02/2017 Date Data Arrived at EDR: 11/07/2017 Date Made Active in Reports: 12/19/2017 Number of Days to Update: 42 Source: Health Care Agency Telephone: 714-834-3446 Last EDR Contact: 11/07/2017 Next Scheduled EDR Contact: 02/19/2018 Data Release Frequency: Quarterly PLACER COUNTY: Master List of Facilities List includes aboveground tanks, underground tanks and cleanup sites. Date of Government Version: 09/05/2017 Date Data Arrived at EDR: 09/06/2017 Date Made Active in Reports: 11/08/2017 Number of Days to Update: 63 Source: Placer County Health and Human Services Telephone: 530-745-2363 Last EDR Contact: 11/30/2017 Next Scheduled EDR Contact: 03/19/2018 Data Release Frequency: Semi-Annually PLUMAS COUNTY: CUPA Facility List Plumas County CUPA Program facilities. Date of Government Version: 10/23/2017 Date Data Arrived at EDR: 11/03/2017 Date Made Active in Reports: 11/15/2017 Number of Days to Update: 12 Source: Plumas County Environmental Health Telephone: 530-283-6355 Last EDR Contact: 11/01/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Varies RIVERSIDE COUNTY: Listing of Underground Tank Cleanup Sites Riverside County Underground Storage Tank Cleanup Sites (LUST). Date of Government Version: 10/11/2017 Date Data Arrived at EDR: 10/12/2017 Date Made Active in Reports: 11/09/2017 Number of Days to Update: 28 Source: Department of Environmental Health Telephone: 951-358-5055 Last EDR Contact: 12/15/2017 Next Scheduled EDR Contact: 04/02/2018 Data Release Frequency: Quarterly Underground Storage Tank Tank List Underground storage tank sites located in Riverside county. Date of Government Version: 10/12/2017 Date Data Arrived at EDR: 10/12/2017 Date Made Active in Reports: 11/08/2017 Number of Days to Update: 27 Source: Department of Environmental Health Telephone: 951-358-5055 Last EDR Contact: 12/15/2017 Next Scheduled EDR Contact: 04/02/2018 Data Release Frequency: Quarterly SACRAMENTO COUNTY: Toxic Site Clean-Up List List of sites where unauthorized releases of potentially hazardous materials have occurred. TC5146125.2s Page GR-38 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Date of Government Version: 08/02/2017 Date Data Arrived at EDR: 10/03/2017 Date Made Active in Reports: 10/06/2017 Number of Days to Update: 3 Source: Sacramento County Environmental Management Telephone: 916-875-8406 Last EDR Contact: 10/03/2017 Next Scheduled EDR Contact: 01/15/2018 Data Release Frequency: Quarterly Master Hazardous Materials Facility List Any business that has hazardous materials on site - hazardous material storage sites, underground storage tanks, waste generators. Date of Government Version: 08/02/2017 Date Data Arrived at EDR: 10/03/2017 Date Made Active in Reports: 11/16/2017 Number of Days to Update: 44 Source: Sacramento County Environmental Management Telephone: 916-875-8406 Last EDR Contact: 10/03/2017 Next Scheduled EDR Contact: 01/15/2018 Data Release Frequency: Quarterly SAN BENITO COUNTY: CUPA Facility List Cupa facility list Date of Government Version: 11/01/2017 Date Data Arrived at EDR: 11/03/2017 Date Made Active in Reports: 11/17/2017 Number of Days to Update: 14 Source: San Benito County Environmental Health Telephone: N/A Last EDR Contact: 11/01/2017 Next Scheduled EDR Contact: 02/19/2018 Data Release Frequency: Varies SAN BERNARDINO COUNTY: Hazardous Material Permits This listing includes underground storage tanks, medical waste handlers/generators, hazardous materials handlers, hazardous waste generators, and waste oil generators/handlers. Date of Government Version: 08/31/2017 Date Data Arrived at EDR: 09/19/2017 Date Made Active in Reports: 11/16/2017 Number of Days to Update: 58 Source: San Bernardino County Fire Department Hazardous Materials Division Telephone: 909-387-3041 Last EDR Contact: 11/06/2017 Next Scheduled EDR Contact: 02/19/2018 Data Release Frequency: Quarterly SAN DIEGO COUNTY: Hazardous Materials Management Division Database The database includes: HE58 - This report contains the business name, site address, business phone number, establishment H’ permit number, type of permit, and the business status. HE17 - In addition to providing the same information provided in the HE58 listing, HE17 provides inspection dates, violations received by the establishment, hazardous waste generated, the quantity, method of storage, treatment/disposal of waste and the hauler, and information on underground storage tanks. Unauthorized Release List - Includes a summary of environmental contamination cases in San Diego County (underground tank cases, non-tank cases, groundwater contamination, and soil contamination are included.) Date of Government Version: 09/05/2017 Date Data Arrived at EDR: 09/06/2017 Date Made Active in Reports: 11/08/2017 Number of Days to Update: 63 Source: Hazardous Materials Management Division Telephone: 619-338-2268 Last EDR Contact: 12/05/2017 Next Scheduled EDR Contact: 03/19/2018 Data Release Frequency: Quarterly TC5146125.2s Page GR-39 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Solid Waste Facilities San Diego County Solid Waste Facilities. Date of Government Version: 10/31/2015 Date Data Arrived at EDR: 11/07/2015 Date Made Active in Reports: 01/04/2016 Number of Days to Update: 58 Source: Department of Health Services Telephone: 619-338-2209 Last EDR Contact: 10/23/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Varies Environmental Case Listing The listing contains all underground tank release cases and projects pertaining to properties contaminated with hazardous substances that are actively under review by the Site Assessment and Mitigation Program. Date of Government Version: 03/23/2010 Date Data Arrived at EDR: 06/15/2010 Date Made Active in Reports: 07/09/2010 Number of Days to Update: 24 Source: San Diego County Department of Environmental Health Telephone: 619-338-2371 Last EDR Contact: 11/29/2017 Next Scheduled EDR Contact: 03/19/2018 Data Release Frequency: No Update Planned SAN FRANCISCO COUNTY: Local Oversite Facilities A listing of leaking underground storage tank sites located in San Francisco county. Date of Government Version: 09/19/2008 Date Data Arrived at EDR: 09/19/2008 Date Made Active in Reports: 09/29/2008 Number of Days to Update: 10 Source: Department Of Public Health San Francisco County Telephone: 415-252-3920 Last EDR Contact: 11/01/2017 Next Scheduled EDR Contact: 02/19/2018 Data Release Frequency: Quarterly Underground Storage Tank Information Underground storage tank sites located in San Francisco county. Date of Government Version: 11/02/2017 Date Data Arrived at EDR: 11/07/2017 Date Made Active in Reports: 12/19/2017 Number of Days to Update: 42 Source: Department of Public Health Telephone: 415-252-3920 Last EDR Contact: 11/01/2017 Next Scheduled EDR Contact: 02/19/2018 Data Release Frequency: Quarterly SAN JOAQUIN COUNTY: San Joaquin Co. UST A listing of underground storage tank locations in San Joaquin county. Date of Government Version: 10/03/2017 Date Data Arrived at EDR: 10/06/2017 Date Made Active in Reports: 10/10/2017 Number of Days to Update: 4 Source: Environmental Health Department Telephone: N/A Last EDR Contact: 12/13/2017 Next Scheduled EDR Contact: 04/02/2018 Data Release Frequency: Semi-Annually SAN LUIS OBISPO COUNTY: CUPA Facility List Cupa Facility List. Date of Government Version: 11/16/2017 Date Data Arrived at EDR: 11/17/2017 Date Made Active in Reports: 12/18/2017 Number of Days to Update: 31 Source: San Luis Obispo County Public Health Department Telephone: 805-781-5596 Last EDR Contact: 11/14/2017 Next Scheduled EDR Contact: 03/05/2018 Data Release Frequency: Varies SAN MATEO COUNTY: TC5146125.2s Page GR-40 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Business Inventory List includes Hazardous Materials Business Plan, hazardous waste generators, and underground storage tanks. Date of Government Version: 09/15/2017 Date Data Arrived at EDR: 09/19/2017 Date Made Active in Reports: 10/17/2017 Number of Days to Update: 28 Source: San Mateo County Environmental Health Services Division Telephone: 650-363-1921 Last EDR Contact: 12/06/2017 Next Scheduled EDR Contact: 03/26/2018 Data Release Frequency: Annually Fuel Leak List A listing of leaking underground storage tank sites located in San Mateo county. Date of Government Version: 09/15/2017 Date Data Arrived at EDR: 09/19/2017 Date Made Active in Reports: 11/09/2017 Number of Days to Update: 51 Source: San Mateo County Environmental Health Services Division Telephone: 650-363-1921 Last EDR Contact: 12/06/2017 Next Scheduled EDR Contact: 03/26/2018 Data Release Frequency: Semi-Annually SANTA BARBARA COUNTY: CUPA Facility Listing CUPA Program Listing from the Environmental Health Services division. Date of Government Version: 09/08/2011 Date Data Arrived at EDR: 09/09/2011 Date Made Active in Reports: 10/07/2011 Number of Days to Update: 28 Source: Santa Barbara County Public Health Department Telephone: 805-686-8167 Last EDR Contact: 12/13/2017 Next Scheduled EDR Contact: 03/05/2018 Data Release Frequency: Varies SANTA CLARA COUNTY: Cupa Facility List Cupa facility list Date of Government Version: 08/07/2017 Date Data Arrived at EDR: 08/10/2017 Date Made Active in Reports: 10/16/2017 Number of Days to Update: 67 Source: Department of Environmental Health Telephone: 408-918-1973 Last EDR Contact: 11/14/2017 Next Scheduled EDR Contact: 03/05/2018 Data Release Frequency: Varies HIST LUST - Fuel Leak Site Activity Report A listing of open and closed leaking underground storage tanks. This listing is no longer updated by the county. Leaking underground storage tanks are now handled by the Department of Environmental Health. Date of Government Version: 03/29/2005 Date Data Arrived at EDR: 03/30/2005 Date Made Active in Reports: 04/21/2005 Number of Days to Update: 22 Source: Santa Clara Valley Water District Telephone: 408-265-2600 Last EDR Contact: 03/23/2009 Next Scheduled EDR Contact: 06/22/2009 Data Release Frequency: No Update Planned LOP Listing A listing of leaking underground storage tanks located in Santa Clara county. Date of Government Version: 03/03/2014 Date Data Arrived at EDR: 03/05/2014 Date Made Active in Reports: 03/18/2014 Number of Days to Update: 13 Source: Department of Environmental Health Telephone: 408-918-3417 Last EDR Contact: 11/21/2017 Next Scheduled EDR Contact: 03/12/2018 Data Release Frequency: Annually TC5146125.2s Page GR-41 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Hazardous Material Facilities Hazardous material facilities, including underground storage tank sites. Date of Government Version: 11/01/2017 Date Data Arrived at EDR: 11/03/2017 Date Made Active in Reports: 12/07/2017 Number of Days to Update: 34 Source: City of San Jose Fire Department Telephone: 408-535-7694 Last EDR Contact: 11/01/2017 Next Scheduled EDR Contact: 02/19/2018 Data Release Frequency: Annually SANTA CRUZ COUNTY: CUPA Facility List CUPA facility listing. Date of Government Version: 01/21/2017 Date Data Arrived at EDR: 02/22/2017 Date Made Active in Reports: 05/23/2017 Number of Days to Update: 90 Source: Santa Cruz County Environmental Health Telephone: 831-464-2761 Last EDR Contact: 11/14/2017 Next Scheduled EDR Contact: 03/05/2018 Data Release Frequency: Varies SHASTA COUNTY: CUPA Facility List Cupa Facility List. Date of Government Version: 06/15/2017 Date Data Arrived at EDR: 06/19/2017 Date Made Active in Reports: 08/09/2017 Number of Days to Update: 51 Source: Shasta County Department of Resource Management Telephone: 530-225-5789 Last EDR Contact: 11/14/2017 Next Scheduled EDR Contact: 03/05/2018 Data Release Frequency: Varies SOLANO COUNTY: Leaking Underground Storage Tanks A listing of leaking underground storage tank sites located in Solano county. Date of Government Version: 09/26/2017 Date Data Arrived at EDR: 09/27/2017 Date Made Active in Reports: 11/10/2017 Number of Days to Update: 44 Source: Solano County Department of Environmental Management Telephone: 707-784-6770 Last EDR Contact: 12/08/2017 Next Scheduled EDR Contact: 03/19/2018 Data Release Frequency: Quarterly Underground Storage Tanks Underground storage tank sites located in Solano county. Date of Government Version: 09/26/2017 Date Data Arrived at EDR: 09/27/2017 Date Made Active in Reports: 11/08/2017 Number of Days to Update: 42 Source: Solano County Department of Environmental Management Telephone: 707-784-6770 Last EDR Contact: 12/08/2017 Next Scheduled EDR Contact: 03/19/2018 Data Release Frequency: Quarterly SONOMA COUNTY: Cupa Facility List Cupa Facility list TC5146125.2s Page GR-42 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Date of Government Version: 09/25/2017 Date Data Arrived at EDR: 09/27/2017 Date Made Active in Reports: 11/16/2017 Number of Days to Update: 50 Source: County of Sonoma Fire & Emergency Services Department Telephone: 707-565-1174 Last EDR Contact: 12/19/2017 Next Scheduled EDR Contact: 04/09/2018 Data Release Frequency: Varies Leaking Underground Storage Tank Sites A listing of leaking underground storage tank sites located in Sonoma county. Date of Government Version: 10/03/2017 Date Data Arrived at EDR: 10/06/2017 Date Made Active in Reports: 11/10/2017 Number of Days to Update: 35 Source: Department of Health Services Telephone: 707-565-6565 Last EDR Contact: 12/19/2017 Next Scheduled EDR Contact: 04/09/2018 Data Release Frequency: Quarterly STANISLAUS COUNTY: CUPA Facility List Cupa facility list Date of Government Version: 11/01/2017 Date Data Arrived at EDR: 11/10/2017 Date Made Active in Reports: 11/16/2017 Number of Days to Update: 6 Source: Stanislaus County Department of Ennvironmental Protection Telephone: 209-525-6751 Last EDR Contact: 10/16/2017 Next Scheduled EDR Contact: 01/29/2018 Data Release Frequency: Varies SUTTER COUNTY: Underground Storage Tanks Underground storage tank sites located in Sutter county. Date of Government Version: 12/01/2017 Date Data Arrived at EDR: 12/04/2017 Date Made Active in Reports: 12/19/2017 Number of Days to Update: 15 Source: Sutter County Department of Agriculture Telephone: 530-822-7500 Last EDR Contact: 12/01/2017 Next Scheduled EDR Contact: 03/19/2018 Data Release Frequency: Semi-Annually TEHAMA COUNTY: CUPA Facility List Cupa facilities Date of Government Version: 11/16/2017 Date Data Arrived at EDR: 11/17/2017 Date Made Active in Reports: 12/18/2017 Number of Days to Update: 31 Source: Tehama County Department of Environmental Health Telephone: 530-527-8020 Last EDR Contact: 11/14/2017 Next Scheduled EDR Contact: 02/19/2018 Data Release Frequency: Varies TRINITY COUNTY: CUPA Facility List Cupa facility list Date of Government Version: 10/23/2017 Date Data Arrived at EDR: 10/24/2017 Date Made Active in Reports: 11/16/2017 Number of Days to Update: 23 Source: Department of Toxic Substances Control Telephone: 760-352-0381 Last EDR Contact: 10/23/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Varies TULARE COUNTY: TC5146125.2s Page GR-43 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING CUPA Facility List Cupa program facilities Date of Government Version: 09/27/2017 Date Data Arrived at EDR: 09/28/2017 Date Made Active in Reports: 10/16/2017 Number of Days to Update: 18 Source: Tulare County Environmental Health Services Division Telephone: 559-624-7400 Last EDR Contact: 12/18/2017 Next Scheduled EDR Contact: 02/19/2018 Data Release Frequency: Varies TUOLUMNE COUNTY: CUPA Facility List Cupa facility list Date of Government Version: 10/24/2017 Date Data Arrived at EDR: 10/25/2017 Date Made Active in Reports: 11/16/2017 Number of Days to Update: 22 Source: Divison of Environmental Health Telephone: 209-533-5633 Last EDR Contact: 10/23/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Varies VENTURA COUNTY: Business Plan, Hazardous Waste Producers, and Operating Underground Tanks The BWT list indicates by site address whether the Environmental Health Division has Business Plan (B), Waste Producer (W), and/or Underground Tank (T) information. Date of Government Version: 09/26/2017 Date Data Arrived at EDR: 10/25/2017 Date Made Active in Reports: 12/07/2017 Number of Days to Update: 43 Source: Ventura County Environmental Health Division Telephone: 805-654-2813 Last EDR Contact: 10/23/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Quarterly Inventory of Illegal Abandoned and Inactive Sites Ventura County Inventory of Closed, Illegal Abandoned, and Inactive Sites. Date of Government Version: 12/01/2011 Date Data Arrived at EDR: 12/01/2011 Date Made Active in Reports: 01/19/2012 Number of Days to Update: 49 Source: Environmental Health Division Telephone: 805-654-2813 Last EDR Contact: 09/27/2017 Next Scheduled EDR Contact: 01/15/2018 Data Release Frequency: Annually Listing of Underground Tank Cleanup Sites Ventura County Underground Storage Tank Cleanup Sites (LUST). Date of Government Version: 05/29/2008 Date Data Arrived at EDR: 06/24/2008 Date Made Active in Reports: 07/31/2008 Number of Days to Update: 37 Source: Environmental Health Division Telephone: 805-654-2813 Last EDR Contact: 11/08/2017 Next Scheduled EDR Contact: 02/26/2018 Data Release Frequency: Quarterly Medical Waste Program List To protect public health and safety and the environment from potential exposure to disease causing agents, the Environmental Health Division Medical Waste Program regulates the generation, handling, storage, treatment and disposal of medical waste throughout the County. Date of Government Version: 09/26/2017 Date Data Arrived at EDR: 10/25/2017 Date Made Active in Reports: 12/07/2017 Number of Days to Update: 43 Source: Ventura County Resource Management Agency Telephone: 805-654-2813 Last EDR Contact: 10/23/2017 Next Scheduled EDR Contact: 02/05/2018 Data Release Frequency: Quarterly TC5146125.2s Page GR-44 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Underground Tank Closed Sites List Ventura County Operating Underground Storage Tank Sites (UST)/Underground Tank Closed Sites List. Date of Government Version: 08/28/2017 Date Data Arrived at EDR: 09/12/2017 Date Made Active in Reports: 09/21/2017 Number of Days to Update: 9 Source: Environmental Health Division Telephone: 805-654-2813 Last EDR Contact: 12/11/2017 Next Scheduled EDR Contact: 03/26/2018 Data Release Frequency: Quarterly YOLO COUNTY: Underground Storage Tank Comprehensive Facility Report Underground storage tank sites located in Yolo county. Date of Government Version: 09/27/2017 Date Data Arrived at EDR: 10/02/2017 Date Made Active in Reports: 11/14/2017 Number of Days to Update: 43 Source: Yolo County Department of Health Telephone: 530-666-8646 Last EDR Contact: 09/27/2017 Next Scheduled EDR Contact: 01/15/2018 Data Release Frequency: Annually YUBA COUNTY: CUPA Facility List CUPA facility listing for Yuba County. Date of Government Version: 11/08/2017 Date Data Arrived at EDR: 11/10/2017 Date Made Active in Reports: 11/16/2017 Number of Days to Update: 6 Source: Yuba County Environmental Health Department Telephone: 530-749-7523 Last EDR Contact: 10/25/2017 Next Scheduled EDR Contact: 02/12/2018 Data Release Frequency: Varies OTHER DATABASE(S) Depending on the geographic area covered by this report, the data provided in these specialty databases may or may not be complete. For example, the existence of wetlands information data in a specific report does not mean that all wetlands in the area covered by the report are included. Moreover, the absence of any reported wetlands information does not necessarily mean that wetlands do not exist in the area covered by the report. CT MANIFEST: Hazardous Waste Manifest Data Facility and manifest data. Manifest is a document that lists and tracks hazardous waste from the generator through transporters to a tsd facility. Date of Government Version: 11/11/2017 Date Data Arrived at EDR: 11/14/2017 Date Made Active in Reports: 12/18/2017 Number of Days to Update: 34 Source: Department of Energy & Environmental Protection Telephone: 860-424-3375 Last EDR Contact: 11/14/2017 Next Scheduled EDR Contact: 02/26/2018 Data Release Frequency: No Update Planned NJ MANIFEST: Manifest Information Hazardous waste manifest information. Date of Government Version: 12/31/2016 Date Data Arrived at EDR: 04/11/2017 Date Made Active in Reports: 07/27/2017 Number of Days to Update: 107 Source: Department of Environmental Protection Telephone: N/A Last EDR Contact: 10/05/2017 Next Scheduled EDR Contact: 01/22/2018 Data Release Frequency: Annually TC5146125.2s Page GR-45 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING NY MANIFEST: Facility and Manifest Data Manifest is a document that lists and tracks hazardous waste from the generator through transporters to a TSD facility. Date of Government Version: 10/01/2017 Date Data Arrived at EDR: 11/01/2017 Date Made Active in Reports: 11/13/2017 Number of Days to Update: 12 Source: Department of Environmental Conservation Telephone: 518-402-8651 Last EDR Contact: 11/01/2017 Next Scheduled EDR Contact: 02/12/2018 Data Release Frequency: Quarterly PA MANIFEST: Manifest Information Hazardous waste manifest information. Date of Government Version: 12/31/2016 Date Data Arrived at EDR: 07/25/2017 Date Made Active in Reports: 09/25/2017 Number of Days to Update: 62 Source: Department of Environmental Protection Telephone: 717-783-8990 Last EDR Contact: 10/16/2017 Next Scheduled EDR Contact: 01/29/2018 Data Release Frequency: Annually RI MANIFEST: Manifest information Hazardous waste manifest information Date of Government Version: 12/31/2013 Date Data Arrived at EDR: 06/19/2015 Date Made Active in Reports: 07/15/2015 Number of Days to Update: 26 Source: Department of Environmental Management Telephone: 401-222-2797 Last EDR Contact: 11/16/2017 Next Scheduled EDR Contact: 03/05/2018 Data Release Frequency: Annually WI MANIFEST: Manifest Information Hazardous waste manifest information. Date of Government Version: 12/31/2016 Date Data Arrived at EDR: 04/13/2017 Date Made Active in Reports: 07/14/2017 Number of Days to Update: 92 Source: Department of Natural Resources Telephone: N/A Last EDR Contact: 12/11/2017 Next Scheduled EDR Contact: 03/26/2018 Data Release Frequency: Annually Oil/Gas Pipelines Source: PennWell Corporation Petroleum Bundle (Crude Oil, Refined Products, Petrochemicals, Gas Liquids (LPG/NGL), and Specialty Gases (Miscellaneous)) N = Natural Gas Bundle (Natural Gas, Gas Liquids (LPG/NGL), and Specialty Gases Miscellaneous)). This map includes information copyrighted by PennWell Corporation. This information is provided on a best effort basis and PennWell Corporation does not guarantee its accuracy nor warrant its fitness for any particular purpose. Such information has been reprinted with the permission of PennWell. Electric Power Transmission Line Data Source: PennWell Corporation This map includes information copyrighted by PennWell Corporation. This information is provided on a best effort basis and PennWell Corporation does not guarantee its accuracy nor warrant its fitness for any particular purpose. Such information has been reprinted with the permission of PennWell. Sensitive Receptors: There are individuals deemed sensitive receptors due to their fragile immune systems and special sensitivity to environmental discharges. These sensitive receptors typically include the elderly, the sick, and children. While the location of all sensitive receptors cannot be determined, EDR indicates those buildings and facilities - schools, daycares, hospitals, medical centers, and nursing homes - where individuals who are sensitive receptors are likely to be located. AHA Hospitals: Source: American Hospital Association, Inc. Telephone: 312-280-5991 The database includes a listing of hospitals based on the American Hospital Association’s annual survey of hospitals. Medical Centers: Provider of Services Listing Source: Centers for Medicare & Medicaid Services Telephone: 410-786-3000 A listing of hospitals with Medicare provider number, produced by Centers of Medicare & Medicaid Services, a federal agency within the U.S. Department of Health and Human Services. TC5146125.2s Page GR-46 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING Nursing Homes Source: National Institutes of Health Telephone: 301-594-6248 Information on Medicare and Medicaid certified nursing homes in the United States. Public Schools Source: National Center for Education Statistics Telephone: 202-502-7300 The National Center for Education Statistics’ primary database on elementary and secondary public education in the United States. It is a comprehensive, annual, national statistical database of all public elementary and secondary schools and school districts, which contains data that are comparable across all states. Private Schools Source: National Center for Education Statistics Telephone: 202-502-7300 The National Center for Education Statistics’ primary database on private school locations in the United States. Daycare Centers: Licensed Facilities Source: Department of Social Services Telephone: 916-657-4041 Flood Zone Data: This data was obtained from the Federal Emergency Management Agency (FEMA). It depicts 100-year and 500-year flood zones as defined by FEMA. It includes the National Flood Hazard Layer (NFHL) which incorporates Flood Insurance Rate Map (FIRM) data and Q3 data from FEMA in areas not covered by NFHL. Source: FEMA Telephone: 877-336-2627 Date of Government Version: 2003, 2015 NWI: National Wetlands Inventory. This data, available in select counties across the country, was obtained by EDR in 2002, 2005 and 2010 from the U.S. Fish and Wildlife Service. State Wetlands Data: Wetland Inventory Source: Department of Fish & Game Telephone: 916-445-0411 Current USGS 7.5 Minute Topographic Map Source: U.S. Geological Survey STREET AND ADDRESS INFORMATION 2015 TomTom North America, Inc. All rights reserved. This material is proprietary and the subject of copyright protection and other intellectual property rights owned by or licensed to Tele Atlas North America, Inc. The use of this material is subject to the terms of a license agreement. You will be held liable for any unauthorized copying or disclosure of this material. TC5146125.2s Page GR-47 GOVERNMENT RECORDS SEARCHED / DATA CURRENCY TRACKING TC5146125.2s Page A-1 geologic strata. of the soil, and nearby wells. Groundwater flow velocity is generally impacted by the nature of the Groundwater flow direction may be impacted by surface topography, hydrology, hydrogeology, characteristics 2. Groundwater flow velocity. 1. Groundwater flow direction, and Assessment of the impact of contaminant migration generally has two principal investigative components: forming an opinion about the impact of potential contaminant migration. EDR’s GeoCheck Physical Setting Source Addendum is provided to assist the environmental professional in 2012VersionDate: 5622818 IMPERIAL BEACH, CATargetPropertyMap: USGS TOPOGRAPHIC MAP 204 ft. above sealevelElevation: 3606465.2UTMY (Meters): 497042.2UTMX (Meters): Zone11UniversalTranverseMercator: 117.031519 - 117 1’ 53.47’’Longitude (West): 32.597385 - 32 35’ 50.59’’Latitude (North): TARGET PROPERTY COORDINATES CHULA VISTA, CA 91911 517 SHINOHARA LANE INDUSTRIAL LAND TARGET PROPERTY ADDRESS GEOCHECK - PHYSICAL SETTING SOURCE ADDENDUM® TC5146125.2s Page A-2 should be field verified. on a relative (not an absolute) basis. Relative elevation information between sites of close proximity Source: Topography has been determined from the USGS 7.5’ Digital Elevation Model and should be evaluated SURROUNDING TOPOGRAPHY: ELEVATION PROFILES Elevation ( ft) Elevation (ft)TP TP 0 1/2 1 Miles Target Property Elevation: 204ft. NorthSouthWest East32729726318213010388125138204262276229229202243238276325158149171165166152186202192204174176188215216207236250234General SouthGeneral Topographic Gradient:TARGET PROPERTY TOPOGRAPHY should contamination exist on the target property, what downgradient sites might be impacted.assist the environmental professional in forming an opinion about the impact of nearby contaminated properties or,Surface topography may be indicative of the direction of surficial groundwater flow. This information can be used to TOPOGRAPHIC INFORMATION collected on nearby properties, and regional groundwater flow information (from deep aquifers).sources of information, such as surface topographic information, hydrologic information, hydrogeologic data using site-specific well data. If such data is not reasonably ascertainable, it may be necessary to rely on other Groundwater flow direction for a particular site is best determined by a qualified environmental professional GROUNDWATER FLOW DIRECTION INFORMATION GEOCHECK - TC5146125.2s Page A-3 GENERALDIRECTIONLOCATION GROUNDWATERFLOWFROMTPMAPID hydrogeologically, and the depth to water table. authorities at select sites and has extracted the date of the report, groundwater flow direction as determined flow at specific points. EDR has reviewed reports submitted by environmental professionals to regulatory EDR has developed the AQUIFLOW Information System to provide data on the general direction of groundwater AQUIFLOW® Search Radius: 1.000 Mile. 1996 Site-specific hydrogeological data gathered by CERCLIS Alerts, Inc., Bainbridge Island, WA. All rights reserved. All of the information and opinions presented are those of the cited EPA report(s), which were completed under a Comprehensive Environmental Response Compensation and Liability Information System (CERCLIS) investigation. Information is inferred in the CERCLIS investigation report(s) Data Quality: No information about a sole source aquifer is availableSoleSourceAquifer: between aquifer(s) underlying the site. Information is not available regarding the hydraulic connectionHydraulicConnection: 110 to 180 feet. Inferred Depth to Water: W TOWARD SAN DIEGO BAY. Groundwater Flow Direction: CAT080010101SiteEPAIDNumber: APPROPRIATE TECHNOLOGIES IISiteName: 1/2 - 1 Mile EastLocationRelativetoTP: 1.25 milesSearchRadius: Site-Specific Hydrogeological Data*: 1996 Site-specific hydrogeological data gathered by CERCLIS Alerts, Inc., Bainbridge Island, WA. All rights reserved. All of the information and opinions presented are those of the cited EPA report(s), which were completed under a Comprehensive Environmental Response Compensation and Liability Information System (CERCLIS) investigation. contamination exist on the target property, what downgradient sites might be impacted. environmental professional in forming an opinion about the impact of nearby contaminated properties or, should of groundwater flow direction in the immediate area. Such hydrogeologic information can be used to assist the Hydrogeologic information obtained by installation of wells on a specific site can often be an indicator HYDROGEOLOGIC INFORMATION YES - refer to the Overview Map and DetailMapIMPERIALBEACH NATIONAL WETLAND INVENTORY NWI Electronic DataCoverageNWIQuadatTargetProperty FEMA FIRM Flooddata06073C2159G FEMA FIRM Flooddata06073C2158G FEMA FIRM Flooddata06073C2157G Additional Panels in search area:FEMA Source Type FEMA FIRM Flooddata06073C2156G Flood Plain Panel at Target Property FEMA Source Type FEMA FLOOD ZONE and bodies of water). Refer to the Physical Setting Source Map following this summary for hydrologic information (major waterways contamination exist on the target property, what downgradient sites might be impacted. the environmental professional in forming an opinion about the impact of nearby contaminated properties or, should Surface water can act as a hydrologic barrier to groundwater flow. Such hydrologic information can be used to assist HYDROLOGIC INFORMATION GEOCHECK - PHYSICAL SETTING SOURCE SUMMARY® TC5146125.2s Page A-4 For additional site information, refer to Physical Setting Source Map Findings. WSW1/8 - 1/4 MileSW2G Varies1/4 - 1/2 MileESE1G Varies1/4 - 1/2 MileESE3 WSW1/8 - 1/4 MileSW1 GENERALDIRECTIONLOCATION GROUNDWATERFLOWFROMTPMAPID GEOCHECK - PHYSICAL SETTING SOURCE SUMMARY® TC5146125.2s Page A-5 Map, USGS Digital Data Series DDS - 11 (1994). of the Conterminous U.S. at 1:2,500,000 Scale - a digital representation of the 1974 P.B. King and H.M. Beikman Geologic Age and Rock Stratigraphic Unit Source: P.G. Schruben, R.E. Arndt and W.J. Bawiec, Geology ROCK STRATIGRAPHIC UNIT GEOLOGIC AGE IDENTIFICATION StratifiedSequenceCategory:CenozoicEra: TertiarySystem: PlioceneSeries: TpCode: (decoded above as Era, System & Series) at which contaminant migration may be occurring. Geologic information can be used by the environmental professional in forming an opinion about the relative speed GEOLOGIC INFORMATION IN GENERAL AREA OF TARGET PROPERTY move more quickly through sandy-gravelly types of soils than silty-clayey types of soils. characteristics data collected on nearby properties and regional soil information. In general, contaminant plumes to rely on other sources of information, including geologic age identification, rock stratigraphic unit and soil using site specific geologic and soil strata data. If such data are not reasonably ascertainable, it may be necessary Groundwater flow velocity information for a particular site is best determined by a qualified environmental professional GROUNDWATER FLOW VELOCITY INFORMATION GEOCHECK - PHYSICAL SETTING SOURCE SUMMARY® EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc. 4 1 2 5 6 5 3 0 1/16 1/8 1/4 Miles TC5146125.2s Page A-7 Min: 5.1 Max: 5.5 Min: 4 Max: 14 50%), Lean Clay limit less than Clays (liquid SOILS, Silts and FINE-GRAINED Soils. 200), Clayey passing No. than 35 pct. Materials (more Silt-Claycobblyloam44inches27inches3 Min: 5.1 Max: 5.5 Min: 0.01 Max: 0.42 50%), Lean Clay limit less than Clays (liquid SOILS, Silts and FINE-GRAINED Soils. 200), Clayey passing No. than 35 pct. Materials (more Silt-Clay clay verycobbly27inches9inches2 5.6 Max: 6 Min: Min: 4 Max: 14 50%), silt. limit less than Clays (liquid SOILS, Silts and FINE-GRAINED 50%), Lean Clay. limit less than Clays (liquid SOILS, Silts and FINE-GRAINED Soils. 200), Silty passing No. than 35 pct. Materials (more Silt-Claycobblyloam9inches0inches1 Soil Layer Information Boundary Classification Saturated hydraulic conductivity micro m/sec Layer Upper Lower Soil Texture Class AASHTO Group Unified Soil Soil Reaction pH) 0inchesDepthtoWatertableMin: 0inchesDepthtoBedrockMin: ModerateCorrosionPotential - Uncoated Steel: Hydric Status: Partially hydric WelldrainedSoilDrainageClass: water table, or are shallow to an impervious layer. Class D - Very slow infiltration rates. Soils are clayey, have ahighHydrologicGroup: cobblyloamSoilSurfaceTexture: OLIVENHAINSoilComponentName: Soil Map ID: 1 in a landscape. The following information is based on Soil Conservation Service SSURGO data. for privately owned lands in the United States. A soil map in a soil survey is a representation of soil patterns Survey (NCSS) and is responsible for collecting, storing, maintaining and distributing soil survey information The U.S. Department of Agriculture’s (USDA) Soil Conservation Service (SCS) leads the National Cooperative Soil DOMINANT SOIL COMPOSITION IN GENERAL AREA OF TARGET PROPERTY GEOCHECK - PHYSICAL SETTING SOURCE SUMMARY® TC5146125.2s Page A-8 WelldrainedSoilDrainageClass: water table, or are shallow to an impervious layer. Class D - Very slow infiltration rates. Soils are clayey, have ahighHydrologicGroup: cobblyloamSoilSurfaceTexture: OLIVENHAINSoilComponentName: Soil Map ID: 3 Min: 7.9 Max: 8.4 Min: 1.4 Max: 4 50%), Lean Clay limit less than Clays (liquid SOILS, Silts and FINE-GRAINED Soils. 200), Clayey passing No. than 35 pct. Materials (more Silt-Clayloam64inches46inches3 Min: 6.6 Max: 8.4 Min: 1.4 Max: 4 50%), Lean Clay limit less than Clays (liquid SOILS, Silts and FINE-GRAINED Soils. 200), Clayey passing No. than 35 pct. Materials (more Silt-Clayclayloam46inches22inches2 Min: 6.6 Max: 8.4 Min: 1.4 Max: 4 50%), Lean Clay limit less than Clays (liquid SOILS, Silts and FINE-GRAINED Soils. 200), Clayey passing No. than 35 pct. Materials (more Silt-Clayclayloam22inches0inches1 Soil Layer Information Boundary Classification Saturated hydraulic conductivity micro m/sec Layer Upper Lower Soil Texture Class AASHTO Group Unified Soil Soil Reaction pH) 0inchesDepthtoWatertableMin: 0inchesDepthtoBedrockMin: HighCorrosionPotential - Uncoated Steel: Hydric Status: Not hydric WelldrainedSoilDrainageClass: textures. moderately well and well drained soils with moderately coarse Class B - Moderate infiltration rates. Deep and moderately deep,Hydrologic Group: clayloamSoilSurfaceTexture: SALINASSoilComponentName: Soil Map ID: 2 GEOCHECK - PHYSICAL SETTING SOURCE SUMMARY® TC5146125.2s Page A-9 0inchesDepthtoWatertableMin: 0inchesDepthtoBedrockMin: ModerateCorrosionPotential - Uncoated Steel: Hydric Status: Not hydric WelldrainedSoilDrainageClass: water table, or are shallow to an impervious layer. Class D - Very slow infiltration rates. Soils are clayey, have ahighHydrologicGroup: cobblyloamSoilSurfaceTexture: OLIVENHAINSoilComponentName: Soil Map ID: 4 Min: 5.1 Max: 5.5 Min: 4 Max: 14 50%), Lean Clay limit less than Clays (liquid SOILS, Silts and FINE-GRAINED Soils. 200), Clayey passing No. than 35 pct. Materials (more Silt-Claycobblyloam59inches42inches3 Min: 5.1 Max: 5.5 Min: 0.01 Max: 0.42 50%), Lean Clay limit less than Clays (liquid SOILS, Silts and FINE-GRAINED Soils. 200), Clayey passing No. than 35 pct. Materials (more Silt-Clay clay verycobbly42inches9inches2 5.6 Max: 6 Min: Min: 4 Max: 14 50%), Lean Clay limit less than Clays (liquid SOILS, Silts and FINE-GRAINED Soils. 200), Silty passing No. than 35 pct. Materials (more Silt-Claycobblyloam9inches0inches1 Soil Layer Information Boundary Classification Saturated hydraulic conductivity micro m/sec Layer Upper Lower Soil Texture Class AASHTO Group Unified Soil Soil Reaction pH) 0inchesDepthtoWatertableMin: 0inchesDepthtoBedrockMin: ModerateCorrosionPotential - Uncoated Steel: Hydric Status: Not hydric GEOCHECK - PHYSICAL SETTING SOURCE SUMMARY® TC5146125.2s Page A-10 0inchesDepthtoWatertableMin: 0inchesDepthtoBedrockMin: HighCorrosionPotential - Uncoated Steel: Hydric Status: Not hydric WelldrainedSoilDrainageClass: movement of water, or soils with moderately fine or fine textures. Class C - Slow infiltration rates. Soils with layers impedingdownwardHydrologicGroup: clayloamSoilSurfaceTexture: LINNESoilComponentName: Soil Map ID: 5 Min: 5.1 Max: 5.5 Min: 4 Max: 14 50%), Lean Clay limit less than Clays (liquid SOILS, Silts and FINE-GRAINED Soils. 200), Clayey passing No. than 35 pct. Materials (more Silt-Claycobblyloam59inches42inches3 Min: 5.1 Max: 5.5 Min: 0.01 Max: 0.42 50%), Lean Clay limit less than Clays (liquid SOILS, Silts and FINE-GRAINED Soils. 200), Clayey passing No. than 35 pct. Materials (more Silt-Clay clay verycobbly42inches9inches2 5.6 Max: 6 Min: Min: 4 Max: 14 50%), silt. limit less than Clays (liquid SOILS, Silts and FINE-GRAINED 50%), Lean Clay. limit less than Clays (liquid SOILS, Silts and FINE-GRAINED Soils. 200), Silty passing No. than 35 pct. Materials (more Silt-Claycobblyloam9inches0inches1 Soil Layer Information Boundary Classification Saturated hydraulic conductivity micro m/sec Layer Upper Lower Soil Texture Class AASHTO Group Unified Soil Soil Reaction pH) GEOCHECK - PHYSICAL SETTING SOURCE SUMMARY® TC5146125.2s Page A-11 Min: 6.6 Max: 7.8 Min: 0.42 Max: 1.4 more), Fat Clay. limit 50% or Clays (liquid SOILS, Silts and FINE-GRAINED Soils. 200), Clayey passing No. than 35 pct. Materials (more Silt-Clayclay14inches0inches1 Soil Layer Information Boundary Classification Saturated hydraulic conductivity micro m/sec Layer Upper Lower Soil Texture Class AASHTO Group Unified Soil Soil Reaction pH) 0inchesDepthtoWatertableMin: 0inchesDepthtoBedrockMin: HighCorrosionPotential - Uncoated Steel: Hydric Status: Not hydric WelldrainedSoilDrainageClass: water table, or are shallow to an impervious layer. Class D - Very slow infiltration rates. Soils are clayey, have ahighHydrologicGroup: claySoilSurfaceTexture: DIABLOSoilComponentName: Soil Map ID: 6 Max: Min: Min: Max: NotreportedNotreported bedrock weathered40inches37inches3 Min: 7.9 Max: 8.4 Min: 1.4 Max: 4 50%), silt. limit less than Clays (liquid SOILS, Silts and FINE-GRAINED Soils. 200), Clayey passing No. than 35 pct. Materials (more Silt-Clayclayloam37inches14inches2 Min: 7.9 Max: 8.4 Min: 1.4 Max: 4 50%), silt. limit less than Clays (liquid SOILS, Silts and FINE-GRAINED Soils. 200), Clayey passing No. than 35 pct. Materials (more Silt-Clayclayloam14inches0inches1 Soil Layer Information Boundary Classification Saturated hydraulic conductivity micro m/sec Layer Upper Lower Soil Texture Class AASHTO Group Unified Soil Soil Reaction pH) GEOCHECK - PHYSICAL SETTING SOURCE SUMMARY® TC5146125.2s Page A-12 STATE DATABASE WELL INFORMATION LOCATION FROMTPWELLIDMAPID Note: PWS System location is not always the same as well location. No PWS System Found FEDERAL FRDS PUBLIC WATER SUPPLY SYSTEM INFORMATION LOCATION FROMTPWELLIDMAPID 1/2 - 1 MileWSWUSGS400001292544 1/4 - 1/2 MileESEUSGS400001292532 FEDERAL USGS WELL INFORMATION LOCATION FROMTPWELLIDMAPID 1.000StateDatabase Nearest PWS within 1mileFederalFRDSPWS 1.000FederalUSGS WELL SEARCH DISTANCE INFORMATION SEARCH DISTANCE (miles)DATABASE opinion about the impact of contaminant migration on nearby drinking water wells. professional in assessing sources that may impact ground water flow direction, and in forming an EDR Local/Regional Water Agency records provide water well information to assist the environmental LOCAL / REGIONAL WATER AGENCY RECORDS Max: Min: Min: Max: NotreportedNotreported bedrock weathered35inches31inches3 Min: 6.6 Max: 7.8 Min: 0.42 Max: 1.4 50%), Lean Clay limit less than Clays (liquid SOILS, Silts and FINE-GRAINED Soils. 200), Clayey passing No. than 35 pct. Materials (more Silt-Clayclay31inches14inches2 Soil Layer Information Boundary Classification Saturated hydraulic conductivity micro m/sec Layer Upper Lower Soil Texture Class AASHTO Group Unified Soil Soil Reaction pH) GEOCHECK - PHYSICAL SETTING SOURCE SUMMARY® TC5146125.2s Page A-13 No Wells Found STATE DATABASE WELL INFORMATION LOCATION FROMTPWELLIDMAPID GEOCHECK - PHYSICAL SETTING SOURCE SUMMARY® EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc.EDR Inc. 4800440400 240 440440440 240400360 320 320280280240240 240 200 200 200160 160 480 4440360320320280280240240 200 160 160 120 120 80 CA TC5146125.2s Page A-15 4 WSW 1/2 - 1 Mile Lower USGS40000129254FEDUSGS Date:07/15/1989 Average Water Depth: Not Reported Deep Water Depth:35 Shallow Water Depth: 18 Groundwater Flow:Varies Site ID:NotReported3 ESE 1/4 - 1/2 Mile Lower 34110AQUIFLOW Ground-water levels, Number of Measurements: 0 ftWellholedepthunits: 182Wellholedepth:NotReportedWelldepthunits: NotReportedWelldepth:19511101Constructiondate: NotReportedAquifertype: NotReportedFormationtype: California Coastal BasinaquifersAquifername: USCountrycode:NGVD29Vertcoordrefsys: Interpolated from topographicmapVertcollectionmethod: feetVertaccmeasureunits: 10Vertaccmeasureval:feetVertmeasureunits: 128Vertmeasureval:NAD83Horizcoordrefsys: Interpolated from DigitalMapHorizCollectionmethod: secondsHorizAccmeasureunits:1HorizAccmeasure: 24000Sourcemapscale:-117.0264944Longitude: 32.5950389Latitude:NotReportedContribdrainageareaunits: NotReportedContribdrainagearea:NotReportedDrainageareaUnits: NotReportedDrainageareavalue:NotReportedHuccode: NotReportedMonlocdesc: WellMonloctype: 018S001W19D001SMonlocname: USGS-323542117013501MonlocIdentifier: USGS California Water ScienceCenterFormalname: USGS-CAOrg. Identifier: 2 ESE 1/4 - 1/2 Mile Lower USGS40000129253FEDUSGS Date:04/12/1990 Average Water Depth: Not Reported Deep Water Depth:35 Shallow Water Depth: 25 Groundwater Flow:WSW Site ID:9UT15841 SW 1/8 - 1/4 Mile Lower 33964AQUIFLOW Map ID Direction Distance Elevation EDR IDNumberDatabase GEOCHECK - PHYSICAL SETTING SOURCE MAP FINDINGS® TC5146125.2s Page A-16 Date: 04/12/1990 Average Water Depth: Not Reported Deep Water Depth:35 Shallow Water Depth: 25 Groundwater Flow:WSW Site ID:9UT15842G SW 1/8 - 1/4 Mile Lower 33964AQUIFLOW Date:07/15/1989 Average Water Depth: Not Reported Deep Water Depth:35 Shallow Water Depth: 18 Groundwater Flow:Varies Site ID:NotReported1G ESE 1/4 - 1/2 Mile Lower 34110AQUIFLOW Ground-water levels, Number of Measurements: 0 ftWellholedepthunits: 1420Wellholedepth:ftWelldepthunits: 1200Welldepth:19960630Constructiondate: NotReportedAquifertype: NotReportedFormationtype: California Coastal BasinaquifersAquifername: USCountrycode:NGVD29Vertcoordrefsys: Interpolated from topographicmapVertcollectionmethod: feetVertaccmeasureunits: 10Vertaccmeasureval:feetVertmeasureunits: 130Vertmeasureval:NAD83Horizcoordrefsys: Interpolated from DigitalMapHorizCollectionmethod: secondsHorizAccmeasureunits:1HorizAccmeasure: 24000Sourcemapscale:-117.0425333Longitude: 32.5950944Latitude:NotReportedContribdrainageareaunits: NotReportedContribdrainagearea:NotReportedDrainageareaUnits: NotReportedDrainageareavalue:NotReportedHuccode: NotReportedMonlocdesc: WellMonloctype: 018S002W24C001SMonlocname: USGS-323542117023301MonlocIdentifier: USGS California Water ScienceCenterFormalname: USGS-CAOrg. Identifier: GEOCHECK - PHYSICAL SETTING SOURCE MAP FINDINGS® TC5146125.2s Page A-17 NotReportedNotReportedNotReportedNotReportedBasement 0%0%100%0.400 pCi/LLivingArea - 2nd Floor 0%0%100%0.677 pCi/LLivingArea - 1st Floor 20 pCi/L% 4-20 pCi/L% <4 pCi/LAverageActivityArea Number of sites tested: 30 Federal Area Radon Information for SAN DIEGO COUNTY, CA Zone 3 indoor average level < 2 pCi/L. Zone 2 indoor average level >= 2 pCi/L and <= 4 pCi/L. Note: Zone 1 indoor average level > 4 pCi/L. Federal EPA Radon Zone for SAN DIEGO County: 3 0491911 4 pCi/LNumTestsZipcode Radon Test Results State Database: CA Radon AREA RADON INFORMATION GEOCHECK - PHYSICAL SETTING SOURCE MAP FINDINGS RADON TOPOGRAPHIC INFORMATION USGS 7.5’ Digital Elevation Model (DEM) Source: United States Geologic Survey EDR acquired the USGS 7.5’ Digital Elevation Model in 2002 and updated it in 2006. The 7.5 minute DEM corresponds to the USGS 1:24,000- and 1:25,000-scale topographic quadrangle maps. The DEM provides elevation data with consistent elevation units and projection. Current USGS 7.5 Minute Topographic Map Source: U.S. Geological Survey HYDROLOGIC INFORMATION Flood Zone Data: This data was obtained from the Federal Emergency Management Agency (FEMA). It depicts 100-year and 500-year flood zones as defined by FEMA. It includes the National Flood Hazard Layer (NFHL) which incorporates Flood Insurance Rate Map (FIRM) data and Q3 data from FEMA in areas not covered by NFHL. Source: FEMA Telephone: 877-336-2627 Date of Government Version: 2003, 2015 NWI: National Wetlands Inventory. This data, available in select counties across the country, was obtained by EDR in 2002, 2005 and 2010 from the U.S. Fish and Wildlife Service. State Wetlands Data: Wetland Inventory Source: Department of Fish & Game Telephone: 916-445-0411 HYDROGEOLOGIC INFORMATION AQUIFLOW InformationSystemR Source: EDR proprietary database of groundwater flow information EDR has developed the AQUIFLOW Information System (AIS) to provide data on the general direction of groundwater flow at specific points. EDR has reviewed reports submitted to regulatory authorities at select sites and has extracted the date of the report, hydrogeologically determined groundwater flow direction and depth to water table information. GEOLOGIC INFORMATION Geologic Age and Rock Stratigraphic Unit Source: P.G. Schruben, R.E. Arndt and W.J. Bawiec, Geology of the Conterminous U.S. at 1:2,500,000 Scale - A digital representation of the 1974 P.B. King and H.M. Beikman Map, USGS Digital Data Series DDS - 11 (1994). STATSGO: State Soil Geographic Database Source: Department of Agriculture, Natural Resources Conservation Service (NRCS) The U.S. Department of Agriculture’s (USDA) Natural Resources Conservation Service (NRCS) leads the national Conservation Soil Survey (NCSS) and is responsible for collecting, storing, maintaining and distributing soil survey information for privately owned lands in the United States. A soil map in a soil survey is a representation of soil patterns in a landscape. Soil maps for STATSGO are compiled by generalizing more detailed (SSURGO) soil survey maps. SSURGO: Soil Survey Geographic Database Source: Department of Agriculture, Natural Resources Conservation Service (NRCS) Telephone: 800-672-5559 SSURGO is the most detailed level of mapping done by the Natural Resources Conservation Service, mapping scales generally range from 1:12,000 to 1:63,360. Field mapping methods using national standards are used to construct the soil maps in the Soil Survey Geographic (SSURGO) database. SSURGO digitizing duplicates the original soil survey maps. This level of mapping is designed for use by landowners, townships and county natural resource planning and management. TC5146125.2s Page PSGR-1 PHYSICAL SETTING SOURCE RECORDS SEARCHED LOCAL / REGIONAL WATER AGENCY RECORDS FEDERAL WATER WELLS PWS: Public Water Systems Source: EPA/Office of Drinking Water Telephone: 202-564-3750 Public Water System data from the Federal Reporting Data System. A PWS is any water system which provides water to at least 25 people for at least 60 days annually. PWSs provide water from wells, rivers and other sources. PWS ENF: Public Water Systems Violation and Enforcement Data Source: EPA/Office of Drinking Water Telephone: 202-564-3750 Violation and Enforcement data for Public Water Systems from the Safe Drinking Water Information System (SDWIS) after August 1995. Prior to August 1995, the data came from the Federal Reporting Data System (FRDS). USGS Water Wells: USGS National Water Inventory System (NWIS) This database contains descriptive information on sites where the USGS collects or has collected data on surface water and/or groundwater. The groundwater data includes information on wells, springs, and other sources of groundwater. STATE RECORDS Water Well Database Source: Department of Water Resources Telephone: 916-651-9648 California Drinking Water Quality Database Source: Department of Public Health Telephone: 916-324-2319 The database includes all drinking water compliance and special studies monitoring for the state of California since 1984. It consists of over 3,200,000 individual analyses along with well and water system information. OTHER STATE DATABASE INFORMATION California Oil and Gas Well Locations Source: Department of Conservation Telephone: 916-323-1779 Oil and Gas well locations in the state. RADON State Database: CA Radon Source: Department of Health Services Telephone: 916-324-2208 Radon Database for California Area Radon Information Source: USGS Telephone: 703-356-4020 The National Radon Database has been developed by the U.S. Environmental Protection Agency USEPA) and is a compilation of the EPA/State Residential Radon Survey and the National Residential Radon Survey. The study covers the years 1986 - 1992. Where necessary data has been supplemented by information collected at private sources such as universities and research institutions. EPA Radon Zones Source: EPA Telephone: 703-356-4020 Sections 307 & 309 of IRAA directed EPA to list and identify areas of U.S. with the potential for elevated indoor radon levels. TC5146125.2s Page PSGR-2 PHYSICAL SETTING SOURCE RECORDS SEARCHED OTHER Airport Landing Facilities: Private and public use landing facilities Source: Federal Aviation Administration, 800-457-6656 Epicenters: World earthquake epicenters, Richter 5 or greater Source: Department of Commerce, National Oceanic and Atmospheric Administration California Earthquake Fault Lines: The fault lines displayed on EDR’s Topographic map are digitized quaternary fault lines, prepared in 1975 by the United State Geological Survey. Additional information (also from 1975) regarding activity at specific fault lines comes from California’s Preliminary Fault Activity Map prepared by the California Division of Mines and Geology. STREET AND ADDRESS INFORMATION 2015 TomTom North America, Inc. All rights reserved. This material is proprietary and the subject of copyright protection and other intellectual property rights owned by or licensed to Tele Atlas North America, Inc. The use of this material is subject to the terms of a license agreement. You will be held liable for any unauthorized copying or disclosure of this material. TC5146125.2s Page PSGR-3 PHYSICAL SETTING SOURCE RECORDS SEARCHED APPENDIX D: QUALIFICATIONS/INSURANCE 800-419-4923 www.PARTNEResi.com Sara A. Gengler Partner Associate Education B.A. in Psychology with minors in business, English, and journalism – Indiana University Highlights 10+ years – writing and editing in the environmental field as follows: Environmental Project Manager conducting Phase I Environmental Risk and Transaction Screen Assessments and writing associated assessment and desktop reports Technical Editor/Proofreader on a government contract working on the U.S. Department of Energy’s Yucca Mountain High-Level Nuclear Waste Storage project License Application Design Selection; SAIC 1998 – 1999) Technical Editor on a government contract working the Environmental Impact Statement for the U.S. Department of Energy’s Yucca Mountain High-Level Nuclear Waste Storage project License Application Design Selection; Jason Associates Corp. (2000 – 2001) 23+ years – writing and editing; journalism Experience Summary Ms. Gengler has been in the environmental services industry for over 10+ years. She has functioned as a Staff Assessor and Environmental Project Manager, conducting Phase I Environmental Risk, Transaction Screen Assessments, writing associated assessment and desktop reports, as well as records search with risk assessments on: multi-family residential and commercial properties that include gas stations, industrial sites, retail centers, motels/hotels. She has performed/conducted more than 1,000 environmental risk assessments. Project Experience Notable projects include: Serving as project manager for environmental assessments of 62 sites throughout Los Angeles County for the enhanced Los Angeles Regional Interoperable Communications System (LA RICS). The assessed sites included: sheriff stations, fire stations, and medical centers that were municipally owned. Served as project manager for a site in Vernon, CA that was represented as a bedding products storage and distribution facility. The site was identified as a decommissioned ammunitions manufacturing plant for the Department of the Army. Features of the site included three underground storage tanks (USTs) which consisted of a 10,000-gallon quench oil, a 20,000-gallon quench oil, and a 1,500-gallon fuel oil UST. The tanks were connected to piping which ran into the adjacent buildings and areas. It further included trenches, grinding machine areas, furnace pits, a phosphate machine containment area, a waste treatment containment area, a cooling tower sump, interior and exterior clarifiers, steam cleaning pits, plating bathes, and numerous other containment areas and sumps. Served as project manager for a 1,650-acre site in Riverdale, CA occupied by a dairy farm with a capacity of approximately 4,000 head of cattle, an onsite biogas project, and numerous active oil Sara A. Gengler 2 | Page wells. For the biogas project, methane gas was derived from manure to provide the gas to a Pacific Gas & Electric (PG&E) power plant. As cow manure decomposed, it produced methane, a greenhouse gas more potent than carbon dioxide. The biogas plant was installed to capture and treat methane to produce renewable gas. To tap the renewable gas from cow manure, manure waste was discharged through piping and furrow irrigation into a pit with an outside perimeter of 152 linear feet. It was then pumped into a 33-foot- deep covered lagoon or “methane digester,” first passing through a screen that filters out large solids. It was lined with plastic to protect the ground water, and the cover, made of high-density polyethylene, was held down at the edges by concrete. Gas collected underneath the cover. Weights on top of the digester channeled the gas to the biogas up-grade plant where it was “scrubbed” of hydrogen sulfide and carbon dioxide. The end product was reportedly nearly 99 percent pure methane. Once it was treated, the gas was injected into PG&E’s pipeline, where it was then transferred to a power plant. Served as technical editor on the Environmental Impact Statement for the U.S. Department of Energy’s Yucca Mountain High-Level Nuclear Waste Storage project License Application Design Selection and on the U.S. Department of Energy’s Yucca Mountain High-Level Nuclear Waste Storage project License Application Design Selection itself. The Yucca Mountain Nuclear Waste Repository was to be a deep geological repository storage facility for spent nuclear fuel and other high-level radioactive waste. The site is located on federal land adjacent to the Nevada Test Site in Nye County, Nevada, approximately 80 miles northwest of the Las Vegas Valley. Federal funding for the site ended in 2011, which leaves US non-governmental entities, such as utilities, without any designated long-term storage site for the high level radioactive waste stored on site at various nuclear facilities around the country. The project was highly contested by the general public and many politicians. The Government Accountability Office stated that the closure was for political, not technical or safety reasons. The Department of Energy (DOE) is reviewing other options for a high-level waste repository and a commission established by the Secretary of Energy released its final report in January 2012. It expressed urgency to find a consolidated, geological repository, and that any future facility should be developed by a new independent organization with direct access to the Nuclear Waste Fund, that is not subject to political and financial control like the DOE. Served as project manager for a ESA on a historic motel in Dalton, IL. Upon site inspection, four pipes of unknown purpose and/or use were observed . At each location was an approximately 1½-inch diameter J-shaped pipe protruding from the ground near a pipe at ground level. The piping was determined to be associated to two underground storage tanks. Publications Contributor in the production of the Environmental Impact Statement for the U.S. Department of Energy’s Yucca Mountain High-Level Nuclear Waste Storage project License Application Design Selection, 2002. 800-419-4923 www.PARTNEResi.com Thomas Petersen, REPA Senior Project Manager Education A.S. in Fire Science Technology, College of San Mateo B.A. in Environmental Studies, California State University, Hayward (Cal State East Bay) Registrations Registered Environmental Property Assessor (REPA) with the National Registry for Environmental Professionals, Cert. #615601 Training Wood Destroying Pest Certification Lead Based Paint and Asbestos trained Sustainable/Green Business trained Highlights Over 20 years of experience in the environmental consulting industry Site Mitigation Phase I Environmental Site Assessments Property Condition Reports Experience Summary Mr. Petersen has over 20 years of experience in the environmental consulting industry and has worked in various disciplines, including: site mitigation, environmental health and safety, regulatory compliance, construction monitoring, subsurface investigation, and environmental and engineering due diligence practices, including Phase I ESAs and PCAs. Mr. Petersen’s primary area of expertise is in the environmental due diligence field, where he has performed and managed thousands of environmental due diligence projects throughout the country. Mr. Petersen has conducted and managed Phase I ESAs on open space, agricultural land, industrial facilities, office buildings and complexes, multi-family developments, government installations, public right-of-ways, shopping malls, retail strips, telecommunication tower sites, service stations, drycleaner facilities and hospitality properties. Most notably, Mr. Petersen has managed due diligence portfolios for varied and demanding clients. In additions to these duties, Mr. Petersen has developed scopes of work, prepared proposals, managed, mentored and trained junior staff, and has regularly provided detailed reports within strict deadlines. Mr. Petersen is familiar with all aspects of due diligence property assessments and reporting standards, including Fannie Mae DUS and Freddie Mac HUD, and is especially knowledgeable on EPA’s All Appropriate Inquiry and ASTM E1527-05. In addition, he has worked with diverse client groups with unique client- specific scopes of work and reporting requirements. Mr. Petersen has completed thousands of Phase I ESAs on multi-family properties, commercial office buildings, shopping centers, gasoline stations, hotels, dry cleaners, auto repair shops, and industrial facilities. Areas of concern included former chemical storage/transfer areas, areas of drainage/deteriorated piping, historical groundwater dispersion wells, and former underground storage tanks systems. Thomas Petersen, REPA 2 | P a g e Mr. Petersen has reviewed and evaluated hundreds of third-party Phase I reports. Currently, Mr. Petersen provides management and QA/QC expertise of Phase I ESAs, transaction screens, and other product types, and is extensively involved in project management and client communications, maintaining an emphasis on providing exemplary client service. Mr. Petersen is responsible for ensuring consistency and quality of due diligence services and ensuring that client-specific requirements are met, as well as the requirements of ASTM and AAI standards. In addition, Mr. Petersen also provides research on specific markets in order to support growth of Partner’s expanding client base. Project Experience Mr. Petersen has worked with national and regional lenders, banks, investors, equity stakeholders, industry, local governments and property owners, including, but not limited to: Bank of America Deutsche Bank City of San Carlos Applied BioSystems NorthMarq Capital Wells Fargo Terra-Gen Power Morgan Stanley EastWest Bank Genentech Met Life ReGen US Bank GE Capital American Tower Legacy Partners SR Commercial ClubCorp NetREIT Finally, Mr. Petersen’s role of managing projects across industrial, residential, retail, and commercial environments, as well as his diverse project experience, is a major contribution to Partner Engineering and Science’s Project Management team. Contact TPetersen@partneresi.com 800-419-4923 www.PARTNEResi.com Mark Lambson Principal Education Bachelor of Arts, Public Administration & Economics, San Diego State University Executive MBA Program, 2000-2003 Highlights Over 20 years of experience in the environmental and engineering consulting industry Property Condition Assessments (PCAs) Fannie Mae, Freddie Mac, and HUD due diligence Experience Summary Mr. Lambson is a true veteran of the commercial real estate services industry. He has over 20 years of experience managing and performing environmental and engineering consulting projects on a national level. Mr. Lambson serves as a Principal for Partner and is located in Partner’s San Diego County office. Mr. Lambson currently provides client management and consulting to a nationwide client base and specializes in advising “equity” clients during the acquisition phase of commercial property transactions in the U.S., Mexico, and Canada. Mr. Lambson has assisted clients on over 10,000 commercial real estate transactions throughout his career. His due diligence resume includes experience at all levels, and includes advising REITs, developers, property managers, retail companies, commercial real estate brokers, mortgage brokers, attorneys, lenders, universities, and real estate investment groups with the following nationwide services: Property Condition Assessments (PCAs) Individual Building System Inspections for Roof, Mechanical Electrical Plumbing (MEP), Elevator, Structure, Façade, and ADA/Accessibility Phase I Environmental Site Assessments (ESAs) Phase II Subsurface Investigations (Soil and groundwater sampling and analysis) Phase III Environmental Remediation Services Asbestos, Lead, Radon, Mold Sampling Seismic and Structural Assessments (PMLs) Energy Audits, Benchmarking, AB1103 Energy Disclosure, and LEED-related services Hydrology, Water Conservation and Efficiency Fannie Mae / Freddie Mac / HUD Due Diligence Geotechnical and Soils Reports Zoning Reports ALTA Surveys Building Sciences Property Condition Assessment, MEP Report, Roof Report, Elevator Report, Structural and Seismic Assessment for a high-profile Class A office campus acquisition in the San Francisco Bay Area ADA Compliance and Accessibility Reviews for a national bank branch portfolio Fannie Mae Property Condition / Physical Needs Assessment services for a 5400-unit multifamily portfolio in Nevada Mark Lambson 2 | P a g e Environmental Assessments Phase I and Phase II Environmental Assessments for a 75-acre aerospace facility in the Northwest United States Over 500 Phase I Environmental Site Assessments for a national fast-food chain Environmental consulting for over 1 million acres of desert land in California, Nevada, and Arizona Land Surveys ALTA Surveys for 2400-unit apartment portfolio in the Midwest Multi-Site Portfolios 113-site office portfolio acquisition for a national REIT 122-site hotel portfolio for a national lending institution 55-site hotel portfolio acquisition for a private investment group 68-site healthcare portfolio acquisition for a national REIT 50-site country club/golf course acquisition for a private investment group Energy and Water Efficiency Energy & Water consulting for a national property owner that operates and manages 30 retail and office centers on the West Coast and Texas Affiliations National Association of Real Estate Investment Trusts (NAREIT) International Council of Shopping Centers (ICSC) U.S Green Building Council (USGBC) Society of Industrial and Office Realtors, San Diego County (SIOR) National Association of Industrial & Office Parks, Southern California (NAIOP) San Diego Habitat Conservancy, Board of Directors. 2010 - 2014 Speaking Bisnow Conference, Panel Moderator, La Jolla, CA, October 2014. Moderated panel on Southern California Real Estate Trends. Globestreet, ICSC Western States Conference, San Diego, CA May 2013. Video interview regarding retail real estate trends and due diligence. Publications Shopping Centers Today, 2010. Authored article on LEED applications for shopping centers and retail assets. Contact mlambson@partneresi.com CITY OF CHULA VISTA OFFICE OF THE CITY C LERK CORRESPONDENCE This email originated from outside of SCS Engineers. Do not click links or open attachments unless you recognize the sender and know the content is safe. From:CHULAVISTACA Support To:O"Neal, Allison Subject:[Records Center] City Records Request :: R000783-062321 Date:Thursday, July 1, 2021 10:27:20 AM Please respond above this line --- RE: PUBLIC RECORDS REQUEST of June 23, 2021., Reference # R000783-062321. Dear Allison ONeal, The City of Chula Vista is in receipt of your June 23, 2021 request for the following public records pursuant to the California Public Records Act (“CPRA”) (Cal. Gov. Code section 6250 et seq.): Hello, Please send all Fire department and industrial waste water records in regards to hazardous materials/wastes, underground or aboveground storage tanks, and unauthorized releases or spills in regards to 517 Shinohara Lane, Chula Vista, CA 91911 APN 644-040-01. Thank you." I have been informed by staff that there are no responsive records to your request. I have also been informed by staff that they believe that they have fully responded to your request; however, if you need additional information I will assist you in your efforts pursuant to Government Code section 6253.1. Please contact the County of San Diego for wastewater records. Should you have any questions please feel free to email this response directly. Sincerely, City Clerk Records Staff BUILDING DEPARTMENT Warning: External Email This email originated from outside of SCS Engineers. Do not click links or open attachments unless you recognize the sender and know the content is safe. From:Daniel Medina on behalf of BuildingDivision To:O"Neal, Allison Subject:RE: Building Permit Records Request - 517 Shinohara Lane Date:Tuesday, July 6, 2021 2:21:25 PM Hi Allison O’Neal, No building permits for the 517 Shinohara were found nor for APN 64404001. Thank you, Daniel A. Medina City of Chula Vista DSD - Building Division 276 Fourth Avenue Chula Vista, CA 91910 619-409-3882 From: O'Neal, Allison <AONeal@scsengineers.com> Sent: Wednesday, June 23, 2021 8:52 AM To: BuildingDivision <BuildingDivision@chulavistaca.gov> Subject: Building Permit Records Request - 517 Shinohara Lane Hello, Please send all building permits for 517 Shinohara Lane, Chula Vista, CA, APN 644-040-01, from 1900 to present, or let me know if there are no records. Thank you, Allison O’Neal Staff Professional SCS Engineers 8799 Balboa Avenue, Suite 290 San Diego, CA 92123 USA 858-583-7763 (W) 858-287-0277 (C) aoneal@scsengineers.com Driven by Client Success www.scsengineers.com 6/23/2021 City of Chula Vista, CA | Citizen Access https://pip.chulavistaca.gov/CitizenAccess/chulavista.aspx?_ga=2.154281840.994235453.1624463257-2143063832.1624292443 1/2 Records General Search General Search Home Planning Land Development Licenses Fire Create an Application Search Applications Schedule an Inspection Show on Map Search for Records Enter only one of the information below to search for records: Permit #; or Address or Parcel or State Contractor License #. Showing 0-0 of 0 Date Permit # Permit Type Permit Description Project Name Status Action Short Note No records found. LogoutAccountManagementReports (2) Cart (0)Collections (0)Logged in as:AllisonONealAnnouncements Search... Building 6/23/2021 City of Chula Vista, CA | Citizen Access https://pip.chulavistaca.gov/CitizenAccess/chulavista.aspx?_ga=2.154281840.994235453.1624463257-2143063832.1624292443 2/2 Permit #:Permit Type: Select-- Start Date: 01/01/1990 End Date: 06/23/2021 Contractor State License Business Name Street #:Direction: Select-- Street Name:Street Type: Select-- Unit #: City:State:Zip: Parcel #: 644-040-01 Search my records only Search All Records Search Clear Notice: Your search returned no results. Please modify your search criteria and try again. Fro To Copyright © 2018 | City of Chula Vista, CA | Building Division | Planning Division | Permits | All Rights Reserved From:O"Neal, Allison To:buildingdivision@ci.chula-vista.ca.us Subject:Building Permit Records Request - 517 Shinohara Lane Date:Wednesday, June 23, 2021 8:51:00 AM Hello, Please send all building permits for 517 Shinohara Lane, Chula Vista, CA, APN 644-040-01, from 1900 to present, or let me know if there are no records. Thank you, Allison O’Neal Staff Professional SCS Engineers 8799 Balboa Avenue, Suite 290 San Diego, CA 92123 USA 858-583-7763 (W) 858-287-0277 (C) aoneal@scsengineers.com Driven by Client Success www.scsengineers.com AIR POLLUTION CONTROL DISTRICT CORRESPONDENCE This email originated from outside of SCS Engineers. Do not click links or open attachments unless you recognize the sender and know the content is safe. From:LUEG, APCDPermits To:O"Neal, Allison Subject:RE: APCD Records Request - 517 Shinohara Lane Date:Thursday, June 24, 2021 10:52:57 AM Hi Allison, There is no record for 517 Shinohara Lane, Chula Vista, CA 91911. Thank you, Radley Salamat | Air Pollution Control Aide | 858-586-2816 From: O'Neal, Allison <AONeal@scsengineers.com> Sent: Wednesday, June 23, 2021 9:12 AM To: Morrison, Freddie <Freddie.Morrison@sdcounty.ca.gov> Subject: APCD Records Request - 517 Shinohara Lane Hello, Please send all APCD records for 517 Shinohara Lane, Chula Vista, CA 91911, APN 644-040-01 or let me know if there are no records. Thank you, Allison O’Neal Staff Professional SCS Engineers 8799 Balboa Avenue, Suite 290 San Diego, CA 92123 USA 858-583-7763 (W) 858-287-0277 (C) aoneal@scsengineers.com Driven by Client Success www.scsengineers.com REGIONAL WATER QUALITY CONTROL BOARD RECORDS WILLIAM A, STEEN & ASSOCIATES 8580 La Mesa Blvd. Suite 102 LA MESA, CALIFORNIA 91941 Phone (619) 460-9000 Fax (619) 460-9005 TO: California Regional Water Quality Control Board 9174 Sky Park Court, Ste. 100 San Diego. CA 92123-4340 LETTER OF TRANSMITTAL DATE 12/10/2007 JOB NO. 6219-101 ATTENTION: RE: 517 Shinohara Lane, Chula Vista, CA WDID #9 373304209 WE ARE SENDING YOU IEI AttachedQ Under separate cover via Mail Shop drawings • Prints • Plans Copy of letter • Change order • the following items: Samples • Specifications o COPIES 1 1 DATE 12-06-07 NO. aiiqo DESCRIPTION <"> r^rr- rc rr. Notice of Termination IT J^o^ per- Photographic Survey Key Map and Photos "Q Of^£ O - O THESE ARE TRANSMITTED as checked below: For approval G Approved as submitted E3 For your use • Approved as noted As requested • Returned for correction For review and comment • Resubmit Submit _ Return _ copies for approval copies for distribution corrected prints FOR BIDS DUE 20_ • PRINTS RETURNED AFTER LOAN TO US REMARKS COPY TO SIGNED: Melissa McVey If enclosures are not as noted, kindly notify us at once SEND TO YOUR LOCAL RWQCB FOR APPROVAL J:', State of California J^ fc/?'*)(/*C G/IJA. State Water Resources Control Board - ONjf^r^^Ai I jZ J'- B0ARt, OF COVERAGE UNDER THE NPDES GENERAL PERMIT NO. CAS000002 ^ ^ /: QQ NOTICE OF TERMINATION iOB] ^ CAS000002 ASSOCIATED WITH CONSTRUCTION ACTIVITY FOR DISCHARGES OF STORM WATER Submission of this Notice of Termination constitutes notice that the owner (and his/her agent) of the site identified on this form is no longer authorized to discharge storm water associated with construction activity by NPDES General Permit No. CAS000002. I. WDID NO. 9 37S304209 II. OWNER Cushman, Lawrence M, COMPANY NAME & Stephen P, CONTACT PERSON Lawrence M, Cushman STREET ADDRESS 2901 Fifth Avenue TITLE Owner CITY San Diego STATE CA ZIP 92103 PHONE 619-299-4160 III. CONSTRUCTION SITE INFORMATION Cushman, Lawrence M. A. DEVELOPER NAME & Stephen P. CONTACT PERSON Lawrence M. Cushman STREET ADDRESS 2901 Fifth Avenue TITLE Owner CITY San Diego CA ZIP 92103 PHONE 619-299-A160 B. SITE ADDRESS 517 Shinohara Lane COUNTY San Diego CITY Chula Vista CA ZIP 92111 PHONE N/A IV. BASIS OF TERMINATION x 1. The construction project is complete and the following conditions have been met. All elements of the Storm Water Pollution Prevention Plan have been completed. Construction materials and wasie have been disposed of properiy. The site is in compliance with all local storm water management requirements. A post-construction storm water operation and management plan is in place. Date of project completion 11 / 26 / 07 2. Construction activities have been suspended, either temporarily or indefinitely and the following conditions have been met. All elements of the Storm Water Pollution Prevention Plan have been completed. Construction materials and waste have been disposed of properly. All denuded areas and other areas of potential erosion are stabilized. An operation and maintenance plan for erosion and sediment control is in place. The site is in compliance with all local storm water management requirements. Date of suspension / / Expected start up date / / 3. Site can not discharge storm water to waters of the United States (check one). SEND TO YOUR LOCAL RWQCB FOR APPROVAL All storm water is retained on site. All storm water is discharged to evaporation or percolation ponds offsite. 4. Discharge of storm water from the site is now subject to another NPDES general permit or an individual NPDES permit. NPDES Permit No. Date coverage began / / 5. There is a new owner of the identified site. Date of owner transfer / / Was the new owner notified of the General Permit requirements? YES NO NEW OWNER INFORMATION COMPANY NAME STREET ADDRESS CITY STATE CONTACT PERSON TITLE ZIP PHONE V. EXPLANATION OF BASIS OF TERMINATION (Attach site photographs - see instructions). The site is no longer required to comply with the General Permit because the construction project has been completed, construction materials and waste have been disposed of, the site is in compliance with the stormwater management requirements of the City of Chula Vista and a post-construction stormwater operation and management plan entitled "Technical Report for 517 Shinohara Lane, Chula Vista, California", dated November 24, 2004 is in place. See attached photographs of the site. VI. CERTlFfcATIOTJ: 1 certify under penalty of law that all storm water discharges associated with construction activity from the identified site that are authorized by NPDES General Permit No. CAS000002 have been eliminated or that I am no longer the owner of the site. I understand that by submitting this Notice of Termination, I am no longer authorized to discharge storm water associated with construction activity under the general permit, and that discharging pollutants in storm water associated with construction activity to waters of the United States is unlawful under the Clean Water Act where the discharge is not authorized by a NPDES permit. I also understand that the submittal of this Notice of Termination does not release an owner from liability for any violations of the general permit or the Clean Water Act. Owner REGIONAL WATEiy BQARn USE ONI Y This Notice of Termination has been reviewed, and I recommend termination of coverage under the subject NPDES general permit Printed Name Region No. Signature Date /_ NOT effective date: Date: / / x TITLE: PHOTOGRAPHIC SURVEY KEY MAP DATE: 12-06-07 JOB NAME: 517 SHINOHARA LN, CHULA VISTA, CA WlilAM A JTEEN & A530CIATES CONSULTING CML ENGWEERS. LAND SURVEYING * PLANNNG JOB NO.: 6219-101 PR0J. ENGR.; WILLIAM A. STEEN SHT. / OF 7 8580 LA MESA BLVD.. SUPTE 102, LA MESA. CALIFORNIA 91941 619) 480-9000 • FAX (619) 460-9005 •