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Q <br /> Limited Phase 11 Subsurface Investigation Report <br /> 902-908 East Scotts Avenue <br /> Stockton,California a ntea g ro u p <br /> Antea Group Project No. UPR82572A <br /> In order to adequately evaluate the presence of metals in shallow soil,Antea Group compared the reported metals <br /> concentrations against their natural occurrence, or typical "background" concentrations, in soils. Each metal <br /> concentration listed in Table 3 is compared to published background data for California soils. The comparison <br /> concentrations are averages from a 1996 report that established a database for 46 trace and major elements <br /> found to occur naturally in 50 benchmark soil samples collected throughout the state of California (Kearney, 1996). <br /> Although they exceed the RSLs, detections of chromium and vanadium in soil were reported at concentrations less <br /> than their respective average background soil concentrations published in the 1996 study. Arsenic concentrations <br /> are greater than the background average, but the reported concentrations fall within the range (min/max) of <br /> naturally occurring metals concentrations listed in the Kearney report(0.6 to 11.0 ppm) with the exception of two <br /> soil samples(620 at 2.0-2.5 feet bgs and B16 at 1.0-1.5 feet bgs). <br /> Antea Group reviewed the metal data to determine site-specific background trends and determine any anomalies <br /> at the site. The 1.0-1.5 feet bgs sample collected in B17,the 2.0-2.5 feet bgs sample collected in B20, and the 1.0- <br /> 1.5 feet bgs collected in B7 all had three or more concentrations of metals that appear to be significantly higher <br /> than the overall sample set.These higher metals concentrations may represent areas of environmental concern. <br /> 3.3.4 Gasoline Range Organics (GRO), Diesel Range Organics (DRO), and Motor Oil <br /> Range Organics (MORO) <br /> The laboratory tested a total of 23 soil samples for GRO and 21 soil samples for DRO and MORO. The detected <br /> concentrations were compared against the California Regional Water Quality Control Board-San Francisco Bay <br /> Region Industrial Environmental Screening Levels (ESLs) for shallow soils and the SSLs. Table 4 includes analytical <br /> summaries of soil analytical results for GRO, DRO, and MORO. <br /> For GRO, only two of the 22 samples tested had detections above the LRL; these detections were also above the <br /> ESL of 83 mg/kg. They were samples collected from 1.0-1.5 feet bgs from boring B3 and B7 and had <br /> concentrations of 2,300 and 1,700 mg/kg, respectively. Both concentrations coincide with the VOC detections also <br /> reported in those samples. <br /> Concentrations of DRO were detected above the LRL in all but two of the 22 submitted for DRO analysis. Six of the <br /> reported concentrations were above the ESL of 83 mg/kg(concentrations ranging from 280 mg/kg to 2,300 mg/kg, <br /> the highest in B7 at a depth of 1.0-2.5 feet bgs). <br /> Eight of the 21 samples submitted for MORO reported concentrations above the LRL; however, only one <br /> concentration exceeded the ESL of 2,500 mg/kg. The sample exceeding the ESL was collected from 1.0-1.5 feet bgs <br /> in B7. This soil sample also exhibited GRO and DRO detections greater than the ESLs. <br /> 3.3.5 Polychlorinated Biphenyls (PCBs) <br /> Antea Group submitted a total of 10 soil samples for PCBs. Of the samples submitted, only one concentration <br /> (0.054 mg/kg in B7 at 1.0-1.5 feet bgs) was detected above LRL, a concentration less than the RSL, ESL, and SSL. <br /> Table 4 includes a summary of the analytical data for PCBs. <br /> 8 www.anteagroup.com <br />