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• Exploratory boring permits were issued November 14, 2005 from the San <br /> Joaquin County Department of Public Health. <br /> Soil Gas Sampling for VOCs and Naphthalene <br /> A total of four borings (SV-1 through SV-4) were advanced in the former drill room at <br /> 1856 Field Avenue by a direct-push technology (DPT) drill rig. As shown on Figure 1, <br /> one boring (SV-1) was placed adjacent to the location of former soil boring S617, while <br /> the remaining three borings were placed within a radius of 20 feet around the location of <br /> SB17. A summary of samples collected is presented in Table 1. <br /> Soil gas samples were collected using the "post-run tubing" (PRT) sampling method. <br /> This method consists of advancing a drive rod to the required depth and then <br /> withdrawing the tip of the probe several inches to expose the surrounding soils. A 3/8- <br /> inch PRT, located inside the drive rod, forms a vacuum- tight seal near the probe tip. <br /> The PRT was purged to remove ambient air. The sampling canister(s) were then <br /> attached to the PRT, and soil vapor samples were collected. <br /> Soil gas samples were collected in general accordance with the guidelines provided <br /> within the document Advisory-Active Soil Gas Investigations developed by DTSC and <br /> the Los Angeles RWQCB (DTSC/RWQCB, 2003). Soil gas samples were collected at a <br /> depth of approximately 5 feet below ground surface (bgs) in each boring. During <br /> installation of the probe, hydrated bentonite was used to seal around the drive rod at <br /> ground surface to prevent ambient air intrusion from occurring. To ensure a <br /> representative sample, a dedicated purging laboratory-supplied 6-liter pre-evacuated <br /> stainless steel Summa canister with flow controller was used to extract three purge <br /> volumes of vapor at a flow rate of approximately 167 millimeters per minute (mL/min) <br /> prior to soil gas sampling in order to rid the tubing of ambient air and allow subsurface <br /> soil gas to enter. A laboratory-supplied 6-liter pre-evacuated stainless steel Summa <br /> canister with a 30-minute flow controller was used to collect soil vapor samples at a flow <br /> rate of approximately 167 mUmin. A duplicate soil vapor sample was collected at SV-2 <br /> and identified as SV-5 for quality assurance and quality control (QA/QC). All soil gas <br /> samples were delivered to Air Toxics Ltd. In Folsom, California, a state-certified <br /> laboratory, for analysis by EPA Method TO-15 (open scan) for VOCs plus naphthalene. <br /> Grab Groundwater Sampling for Naphthalene and Bis(2-ethylhexyl)phthalate <br /> Upon the completion of soil vapor sampling, each boring was further advanced by the <br /> DPT drill rig to a depth of approximately 20 feet bgs. A slotted PVC casing with filter <br /> sock was inserted into each boring, and grab groundwater samples were collected from <br /> each location using a peristaltic sampling pump. <br /> A duplicate groundwater sample was collected at SV-1 and identified as SV-5. Triple <br /> volumes of the sample collected at SV-4 were supplied to the laboratory for matrix <br /> spike/matrix spike duplicate (MS/MSD) analysis. Additionally, an equipment blank was <br /> collected by drawing laboratory-supplied deionized water through new tubing using the <br /> peristaltic pump. The groundwater samples were delivered to Entech Analytical Labs, <br /> Inc. in Santa Clara, California, a state-certified laboratory, in an iced cooler for <br /> naphthalene and bis(2-ethylhexyl)phthalate analyses using EPA Method 8270C. <br /> Page 2 of 4 January 2006 <br />