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Groundwater Elevation Data <br /> • Depth to groundwater was obtained from the existing groundwater monitor wells at the site using <br /> a water level indicator graduated to 0 01 foot The depth to groundwater measurement was <br /> converted to a groundwater elevation for each well and used to construct a groundwater elevation <br /> contour map (Figure 2), and calculate the local groundwater flow direction and hydraulic gradient <br /> Groundwater at the site was measured at depths between 66 80 to 80 35 feet below ground surface <br /> (bgs) The groundwater potentiometric surface elevation averaged approximately 29 24 feet bgs <br /> during this momtonng event The groundwater elevation has decreased approximately 0 51 feet since <br /> the last sampling event in July 1999 The groundwater flow direction during this reporting period <br /> is toward the south/southwest with a hydraulic gradient of approximately 0 03 ft /ft A summary of <br /> data regarding groundwater levels measured through November 24, 1999 is presented in Table 1 <br /> Copies of field observations documenting work performed at the site is presented in Attachment I <br /> Groundwater Analytical Results <br /> The distribution of groundwater sample analytical results obtained from monitor wells at the site on <br /> November 24, 1999, is presented on Figure 2 and summarized in Table 2 TPHg and BTEX were <br /> present at detectable concentrations in eight of the ten samples submitted for analysis Chemical <br /> analytical results indicate the highest concentrations of TPHg and benzene are in the vicinity of <br /> monitor wells MW-1, MW-3 and MW-4 TPHg concentrations in groundwater samples ranged from <br /> 6,320 micrograms per liter (ug/L) in monitor well MW-1, to less than detectable levels in samples <br /> collected from monitor wells MW-8 and MW-10 Benzene concentrations ranged from below the <br /> laboratory method detection hmit in monitor wells MW-1, MW-8 and MW-10, to 193 ug/L in MW-4 <br /> MTBE concentrations in groundwater samples ranged from below the laboratory method detection <br /> limit in monitor wells MWA, MW-3 and MW-7 through MW-10, to 17 5 ug/L in a sample collected <br /> from monitor well MW-4 Attachment II contains photocopies of the laboratory analytical reports <br /> and the chain-of-custody form <br /> Purge Water <br /> Purge water generated during groundwater purging is currently contained on-site in Department of <br /> Transportation rated 55-gallon drums and will be removed to a disposal/recycling facility <br /> SITE REMEDIATION <br /> Soil Remediation System Construction <br /> A corrective action plan, including the installation and operation of an air sparging and soil vapor <br /> extraction and treatment system, has been approved by San Joaquin County Public Health Services <br /> The soil vapor extraction system (VES) consists of seven soil vapor extraction (SVE) wells (W-1, <br /> W-3 through W-8), two groundwater monitor wells (MW-1 and MW-3) and four air sparge wells <br /> (AS-1 through AS-4) with catalytic oxidation treatment at the site Construction of the remediation <br /> system was completed at the site in December 1999 A Site Plan depicting the locations of the <br /> remediation wells, subsurface piping, and remediation equipment compound is included as Figure 3 <br /> Initial start-up air discharge compliance testing was completed on December 13, 1999 Initial <br /> • D Alin OLML kerordQ4 99 2 SFCOR <br /> February <br /> 077 41737 003 25 2000 <br />