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Ms Marla D Guenslcr <br /> Exxon Company, U S A <br /> August 20, 1997 <br /> Page 4 <br /> summarized in Table 2, and a copy of the laboratory analytical report for the May 30, 1997, sampling <br /> event is presented in Enclosure E <br /> SVE Pilot Testing Procedure <br /> Due to additional soil excavation activities that occurred after an initial SVE test was conducted <br /> (March 3, 1995), a second SVE test was performed to re-evaluate remedial options for the site Results <br /> of the first SVE test are included in a Delta report dated Apnl 12, 1995 On June 5, 1997, a SVE test <br /> was conducted on each of two vapor extraction wells (VEW-I and VEW-3) VEW-2 was not used <br /> since it had been destroyed during the additional soil excavation activities The first three hour test was <br /> conducted on VEW-3 and the second three hour test was conducted on VEW-1 A vacuum was <br /> induced in each of the test wells using a portable blower To reduce hydrocarbon emissions, the blower <br /> exhaust was routed through two 200-pound vapor phase granular activated carbon (GAC) columns <br /> prior to atmospheric discharge Field measurements collected during the tests included wellhead <br /> vacuum in VEW-1, VEW-3, and MW-1 through MW-3, soil vapor concentrations, airflow velocities, <br /> temperatures, lower explosive limit (LEL) values, oxygen content, and depth to ground water in the test <br /> wells Field monitoring data for the individual SVE tests are included in Enclosure F <br /> To assess the radial vacuum influence from the test conducted on VEW-3, vacuum measurements were <br /> recorded in VEW-I, MW-2, and MW-3 which are located approximately 45, 100, and 38 feet from <br /> VEW-3, respectively To assess radial vacuum influence from the test conducted on VEW-1, vacuum <br /> measurements were recorded in VEW-3, MW-1, and MW-2 which are located approximately 45, 25, <br /> and 95 feet from VEW-2, respectively <br /> GAC influent and effluent TPPH as hexane concentrations were monitored on an hourly basis with the <br /> use of a portable flame ionization detector (FID) with a methane filter In an effort to confirm FID <br /> measurements, vapor samples were collected in tedlar bags during each SVE test for laboratory <br /> analyses of BTEX and TPPH as gasoline using EPA Methods 8020 and 8015 Modified, respectively <br /> Influent samples were collected at the beginning and the end of each test period Effluent samples were <br /> collected at the start of the first test and the end of the second test <br /> SVE Pilot Testing Results <br /> Filtered FID measurements of TPPH concentrations ranged from 3 5 to 0 4 parts per million by volume <br /> (ppmv) during the test conducted on VEW-3 During the second test conducted on VEW-1, the filtered <br /> FID measurements ranged from 590 to 150 ppmv Field monitoring data is included in Enclosure F <br /> Analytical results from influent samples collected during the beginning and end of the test on VEW-3 <br /> as well as both effluent samples for the entire test did not report BTEX and TPPH as gasoline <br /> concentrations above the laboratory's Iimits of detection Analytical results from influent samples <br /> collected during the SVE test conducted on VEW-1 reported TPPH as gasoline concentrations that <br />. ranged from 93 to 73 ppmv, with a calculated average of 83 ppmv Benzene concentrations for both <br /> influent samples collected during the second test conducted on VEW-1 were reported below the <br /> laboratory's limits of detection (<0 16 ppmv) Analytical results are presented in Table 7 A copy of <br /> the analytical reports is included in Enclosure G <br />