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L <br /> f <br /> Mr. Siddarth Sewalia <br /> 1 February 2011 <br /> Page 3 <br /> valve to establish and maintain an air-tight seal. A soil gas probe construction diagram is <br /> presented as Figure 3. <br /> After construction, the soil gas probes will be allowed to equilibrate for at least 30 minutes prior <br /> to purging and sampling. Figure 4 illustrates the soil gas sampling equipment setup. Prior to <br /> sampling, a leak check and purging will be performed at each location. Each probe will be <br /> purged using a 1-liter Tedlar bag and lung box. Field screening will be performed using a <br /> photoionization detector (PID) and oxygen/carbon dioxide/methane meter for a minimum of <br /> three successive Tedlar bag purge samples to confirm steady readings before sample collection. <br /> Helium will be used as a tracer gas to check that no significant amount of atmospheric air enters <br /> the soil gas sample through the annular seal between the ground surface and probe. To test for <br /> potential leakage, a shroud will be placed around the ground surface of each probe and helium <br /> gas will be added to the shroud during the purging and field screening process. The <br /> concentration of helium in the shroud will be recorded with a portable helium detector to confirm <br /> that the shroud contains a minimum of 10%helium. Soil gas samples collected in the Tedlar bag <br /> will be screened to confirm that the concentration of helium in each sample was less than 5% of <br /> the concentration in the shroud, verifying that the Tedlar bag samples consist of at least 95% soil <br /> gas prior to collection of samples for laboratory analysis. If helium tracer data indicates a leak, <br /> the probe fittings will be tightened as needed to obtain a representative soil gas sample. <br /> Following purging and leak testing, soil gas samples will be collected using 6-liter Summa <br /> canisters. The initial canister vacuum will be measured before sampling to confirm the integrity <br /> of the canisters prior to sample collection. The canister flow controllers will be set at a flow rate <br /> of 200 milliliters per minute (ml/min) so that sample collection will not impose an excessive <br /> vacuum on the soil gas probes. Soil gas will be collected over a period of approximately 5 <br /> minutes, after which time the canister will be closed and disconnected from the probe. After <br /> sample collection, the residual vacuum in each canister will again be measured and recorded. <br /> For quality assurance/quality control, a split sample will be collected from one location and sent <br /> to the analytical laboratory as a blind duplicate. The sample containers will be labeled, logged <br /> on a chain-of-custody form, and transported under chain-of-custody procedures to Air Toxics, <br /> Ltd., of Folsom, California(Air Toxics), for analysis. <br /> Following sample collection, the soil gas probes will be manually pulled from the borehole, the <br /> boreholes will be sealed according to County requirements, and the surface of each borehole will <br /> be completed with cement or asphalt to match the surrounding ground surface. <br /> P:\PRJ2003REM\Wilbur-Ellis\Wr0250(JTF)\STOCKTON\S IT Vapor Sampling\Work Plan\JTF Stockton Off-Site Soil Gas Sampling Work Plaa.docx <br /> engineers I scientists I innovators <br />