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Sampling and Analysis Plan for <br /> Phase II Environmental Site Assessment <br /> South Pointe Property: 701, 705, 833, 855 West Weber Avenue <br /> Stockton, California <br /> Project and Data Quality Objectives <br /> May 17, 2021 <br /> will be compared to UESPA Regional Screening Levels (RSLs, November 2020). For compounds <br /> with no established SLs or RSLs, soil data will be compared to Environmental Screening Levels <br /> (ESLs)established by the San Francisco Bay Regional Water Quality Control Board (RWQCB, <br /> 2019). <br /> • Soil vapor data will be compared to RWQCB ESLs. <br /> Steps 6 and 7— Data Collection Plan and Data Quality Objectives Analysis <br /> Soil vapor conditions will be assessed by gridding the site into 100- by 100-foot sections and collecting <br /> passive vapor samples at each of the intersecting nodes. Based on professional experience, this <br /> sampling effort is appropriate for`reconnaissance level' assessment of soil gas conditions across the 9- <br /> acre site where there are no currently known or suspected sources of impacts to soil vapor. This 100-foot <br /> grid spacing is also consistent with specifications provided by the manufacturer of the passive soil vapor <br /> samplers (Beacon Environmental; their SOP and laboratory accreditation certificate are included in <br /> Appendix C). Samples will be analyzed by the laboratory and results used to guide the collection of active <br /> vapor samples at up to an estimated ten locations. Active soil vapor samples will be collected from <br /> multiple depths, anticipated to be approximately 5 and 12 feet below grade. Soil vapor samples will be <br /> analyzed by the analytical laboratory to quantify concentrations of VOCs in soil vapor. <br /> Soil conditions will be assessed by advancing test pits at 20 locations for collection of soil samples. Test <br /> pits will be advanced at locations where previous data indicate incomplete vertical delineation of OCPs in <br /> soil. Test pits will be extended to an anticipated target depth of 10 feet below grade to examine shallow fill <br /> materials (previously identified to between ground surface and approximately 5 feet bgs across most of <br /> the site)and underlying native materials. It is anticipated that three soil samples will be collected from <br /> each test pit, one from the mid-point of observed fill materials, and two from underlying native materials. <br /> Samples will be collected into laboratory-supplied containers and analyzed for OCPs and lead by an <br /> accredited analytical laboratory. <br /> The sampling and analysis plan has been designed using best professional judgement to be <br /> representative of the area being assessed. Analytical practices will adhere to industry technical <br /> standards. Soil samples will be analyzed for OCPs by USEPA Method 8081 B. Soil vapor samples will be <br /> collected in accordance with current guidance published by California DTSC (Advisory, Active Soil Gas <br /> Investigations, July 2015) and analyzed by USEPA Method TO-15. Passive soil vapor samples will be <br /> collected using American Society for Testing and Materials (ASTM)-compliant sample modules and <br /> analyzed using USEPA Method 8260C. Measurement error, rather than sampling error, is deemed the <br /> primary factor affecting any decision error. Validated definitive data will be required to limit measurement <br /> error. Sampling error will be limited to the extent practicable by following approved USEPA methods and <br /> applicable SOPs. In addition, the following conditions apply to the sampling plan. <br /> • It is assumed that current and future use of the site will be for mixed use residential and <br /> commercial. Exposure pathways of concern include potential direct contact with shallow soil, <br /> inhalation of dust particulates during redevelopment activities, and ingestion of soil by future <br /> `1 Project No.: 185704833.5.3&5.4 3.3 <br />