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4< <br /> Ms Margaret Lagorio S E C ® R <br /> August 1, 2005 <br /> Page 3 <br /> � <br /> encountered between 55 and fit feet bgs The vapor extraction wells were constructed of <br /> 4-inch PVC casing with a 25-foot screened interval and set between 49 and 50 feet bgs <br /> Groundwater was not encountered during the installation of these wells Laboratory <br /> 9 <br /> analysis of collected sod samples detected the presence of TPHg and BTEX compounds <br /> (RESNA, 1992) <br /> Additionally, in March 1992, RESNA performed a vapor extraction test (VET) The highest <br /> observed vacuum was 0 60 inches of water in VW-4 while VW-2 was undergoing an air <br /> flow rate of 81 cubic feet per minute (cfm) and a vacuum of more than 50 inches of water <br /> RESNA concluded that soil vapor extraction was a viable means to remediate petroleum <br /> hydrocarbon contamination in the vadose zone Two additional vapor extraction wells were <br /> installed (VW-5 and VW-6) (RESNA, 1992) <br /> In August 1992, RESNA installed five additional offsite monitoring wells (MW-9 through <br /> MW-13) and one onsite groundwater extraction well (PTW-1) The offsite wells were <br /> constructed of 2-inch PVC casing with a 20-foot screened interval and set at depths <br /> ranging from 70 to 72 feet bgs PTW-1 was constructed of 6-inch PVC casing with a <br /> 20-foot screened interval and set at 72 5 feet bgs Laboratory analysis of the soil samples <br /> did not detect petroleum hydrocarbons (RESNA, 1991) <br /> Additionally in August 1992, RESNA performed an aquifer test utilizing PTW-1 as the ' <br /> extraction well The results identified a water bearing zone between 55 and 75 feet that is <br /> heterogeneous, anisotropic, and unconfined The parameters of the aquifer were <br /> calculated to be 0 4 to 0 8 square feet per minute (Wlmin) for the transmissivity and a 5 to <br /> • 10 percent specific yield (RESNA, 1992) <br /> A vapor extraction system (VES) utilizing a catalytic oxidizer unit was in operation at the site <br /> from September 1994 through the second quarter of 2001 By the end of the second <br /> quarter of 2001, approximately 14,794 pounds of TPHg and 183 pounds of benzene were <br /> extracted and treated The remediation method was revised in late 2001, from full-time <br /> VES using the catalytic oxidizer unit to ozone sparging ' <br /> In February 1996, wells MW-3, MW-10, MW-12, and MW-13 were abandoned at the <br /> request of the City of Stockton This work was performed to facilitate reconstruction of the <br /> intersection and widening of Pacific Avenue <br /> In August 1999, Gettler Ryan (GR) installed three groundwater monitoring wells (MW-14 <br /> through MW-16), one groundwater sparging well (VW-7) and advanced one soil boring <br /> (VW-9) These groundwater monitoring wells replaced the wells that were abandoned in <br /> February 1996 <br /> In April 2000, the service station building and all related facilities were removed from the <br /> site, including two 12,000-gallon double-wall steel gasoline USTs Soil samples were <br /> collected from beneath the USTs, product lines, and dispenser islands Soil thought to be <br /> potentially impacted was over-excavated A total of approximately 200 cubic yards of soil <br /> was excavated from beneath the northwest and southeast dispenser islands and product <br /> lines immediately north of the west UST In addition, the UST pit was excavated to a depth <br /> of 21 feet bgs Soil samples were collected, analyzed, and reported as non-detect for <br /> • petroleum constituents except for 2 73 parts per million (ppm) of TPHg beneath the <br /> northeast dispenser island at 4 75 feet bgs, and 38 3 ppm of TPHg and 0 125 ppm of r <br /> 8981 2Q2005 QSSR doc SECOR International Incorporated <br /> 3' <br /> r <br /> i <br />