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SUPPLEMENTAL SITE INVESTIGATION WORK PLAN <br /> South Pointe Property <br /> Stockton, California <br /> Site Background <br /> The conceptual site model developed by WKA postulated that elevated concentrations of OCPs <br /> and lead are generally associated with historical materials handling processes and incidental spills <br /> along the railroad spur historically present in the central portion of the site. Excavation during soil <br /> assessment activities identified fill materials (indicated by the presence of wood, metal, brick, <br /> concrete, and asphalt debris) believed to be associated with demolition of historical structures at <br /> the site. <br /> Test pits advanced by Stantec encountered evidence of fill materials from ground surface to <br /> depths ranging from approximately 2 to 8 ft bgs. Fill materials consisted of native soils (generally <br /> sandy silt and gravel) mixed with wood, metal, brick, concrete, and asphalt debris. The pesticide <br /> reported most frequently in soil samples was dieldrin and the compounds aldrin, DDD, DDE, DDT, <br /> endrin, chlordane, and toxaphene were detected in one or more soil samples. Only <br /> concentrations of dieldrin and toxaphene exceeded their respective screening levels in one or <br /> more samples. Locations of samples with OCPs exceeding screening criteria are illustrated on <br /> Figure 3 in Appendix B. Concentrations of lead reported in 13 samples exceeded the unrestricted <br /> screening level of 80 milligrams per kilogram (mg/kg). The locations of these samples, with <br /> concentrations ranging from 80.1 to 219 mg/kg, are illustrated on Figure 3 in Appendix B. <br /> The 2021 investigation provided additional vertical delineation of OCPs and lead in soil beneath <br /> portions of the conceptual remediation area identified by WKA. This investigation confirmed <br /> previous findings regarding the presence of fill materials along the former rail line and confirmed <br /> that elevated concentrations of OCPs and lead are generally associated with these materials. <br /> The depth of fill materials ranges from approximately 2 to 11 ft bgs, and accumulations of fill are <br /> thickest in the central portion of the site. Based on current and historical data, soil chemical <br /> impacts exceeding screening criteria are limited to the upper ten feet. <br /> In evaluating historical data, Stantec compared historical and current chemical data to <br /> updated soil screening criteria for unrestricted use established by California DTSC (historical <br /> data, compared against current screening levels, are included in Appendix A with the historical <br /> data collected by WKA). Using this comparison approach, Stantec developed a conceptual soil <br /> remediation area generally conforming to the remediation area identified by WKA in 2007.This <br /> area, depicted on Figure b in Appendix B, illustrates the extent of soil/fill at the site with <br /> concentrations of OCPs and/or lead exceeding unrestricted site use screening criteria. <br /> Soil Vapor Conditions <br /> The passive soil vapor survey identified several VOCs and total petroleum hydrocarbons (TPH) in <br /> the C10 to C15 carbon chain range in one or more of the passive vapor modules. Petroleum <br /> hydrocarbons reported as TPH C10-C15 was the most commonly-detected compound, <br /> followed by benzene with nine detections. Stantec requested that Beacon (supplier of the <br /> passive vapor modules) produce isoconcentration maps for these compounds. As illustrated on <br /> Figure 4 in Appendix B, two 'hot spots' of relatively elevated TPH mass were identified in the <br /> northern portion of the site. These were generally not accompanied by elevated concentrations <br /> of benzene, where the highest concentrations were observed in the southern portion of the site. <br /> 2.6 <br />