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a , <br /> 27 January 2006 <br /> AGE-NC Project No 98-0500 <br /> Page 2 of 10 <br /> Two deep-screened (145 feet to 150 feet bsg) depth-discrete wells located in the former <br /> underground storage tank (UST) area and the former dispenser area, MW-34, MW-36, <br /> MW-39,MW-42,MW-44,MW-46,and MW-48 are screened In the sixth hydrogeologic unit <br /> (HU6), <br /> • Deep-screened well MW-37 (195 feet to 200 feet bsg) is screened in the seventh <br /> hydrogeologic unit(HU7), and <br /> • Deep-screened well MW-35 (225 feet to 245 feet bsg) is screened across the seventh and <br /> eighth hydrogeologic units (HU7 and HU8, respectively) <br /> A brief summary of background information and a basic site conceptual model is included in <br /> Appendix A Field work was performed in accordance with guidelines established by the <br /> CVRWQCB for subsurface investigation of contaminated sites The monitoring well designations <br /> were reassigned during the final quarter of 2003 in a sequential order, the renumbered wells are <br /> presented in Table 3 and on Figure 2 <br /> • 2.0. SOIL-VAPOR EXTRACTION OPERATION AND MONITORING RESULTS <br /> A catalytic oxidizer soil-vapor extraction(SVE)unit is connected to a total of twenty-six extraction <br /> wells on the eastern and western portions of the site A total of nineteen individual SVE wells <br /> (VW-6A through VW-1513) and monitoring well MW-1 are located on the eastern side of the site <br /> and are connected aboveground to the SVE unit using 2-inch diameter, Schedule 40 <br /> polyvinylchloride (PVC)piping and 2-inch ball valves to control flow from individual wells Four <br /> SVE wells(VW-lA through VW-213) and two monitoring wells (MW-15 and MW-16)are located <br /> on the western edge of the site and are connected below grade near the wells and then above grade <br /> through the building to the SVE unit using 2-inch diameter, Schedule 40 PVC piping However,due <br /> to pipe damage and excessive vapor collection within the site, the western wells were not utilized <br /> this quarter <br /> The piping (influent line) was routed through 3-inch diameter, Schedule 40 PVC piping manifold <br /> and then through a moisture knockout vessel to a 20-horsepower,maximum 500 standard cubic feet <br /> per minute (scfm) blower Sampling ports were installed upstream of the vacuum blower inlet to <br /> recover influent soil-gas vapor stream samples,and downstream of the catalytic converter to recover <br /> effluent stream samples to monitor the efficiency of hydrocarbon destruction A Magnehelic vacuum <br /> gauge was attached to the inlet of the SVE unit to measure the inlet potential pressure Field <br /> measurements, recorded at regular intervals, are summarized in Table 1 <br /> SVE-system operations are in accordance with San Joaquin Unified Air Pollution Control District <br /> (APCD) permit-5861-1-0 <br /> Advanced GeoEnvironmental,Inc <br />