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Mr Jeffrey Wong <br /> Page 2 of 7 <br /> 2.0 BACKGROUND INFORMATION <br /> 2.1 Site Description and Hydrogeologic Setting <br /> The site is located in east central Stockton approximately one mile west of Highway 99 (Figure 1) <br /> The nearest naturally occurring body of surface water is the Calaveras River, located approximately <br /> one mile to the north Approximately 1/2 mile north of the property, between the property and the <br /> Calaveras River is the Stockton Diverting Canal, a tributary to the Raver Surface elevation at the <br /> site is approximately twenty-one feet above sea level <br /> Based upon published data from the San Joaquin County Flood Control and Water Conservation <br /> District (Spring 1997 Groundwater Report), groundwater was expected to have been encountered at <br /> a depth of approximately 55 feet below grade in the site vicinity Data from an adjacent property <br /> reveal that historic low groundwater occurred in 1992 at approximately 85 feet below grade Water <br /> levels may have reached historic highs in early 1999 when the depth to water in the site vicinity was <br /> approximately 36-38 feet below grade According to the Flood Control District reports, <br /> groundwater flow has been predominantly toward the northeast although the property is located <br /> within an area subject to repeated variations in flow direction and gradient Groundwater flow at <br /> the adjacent site has varied from southwesterly to northeasterly over a period of less than ten years <br /> 2.2 Underground Storage Tank Removal and Soil Sampling <br /> On April 12, 1989, four USTs(one 2,000 gallon, two 550 gallon and one 300 gallon)were removed <br /> from the subject site by North Cal Construction of Stockton, California The contents of the USTs <br /> apparently had consisted of gasoline One soil sample was collected from beneath each of the <br /> smaller USTs at depths ranging from 9 to 10 feet Two samples were collected at depths of 11 5 <br /> feet from beneath the 2,000 gallon UST In addition one soil sample was collected from a depth of <br /> 3 feet beneath a product line The samples were submitted to State-Certified FGL Environmental <br /> Laboratories for analysis Each sample was analyzed for total petroleum hydrocarbons (TPH) using <br /> modified EPA Method 8015, for benzene, toluene, ethylbenzene and xylenes (BTEX) and ethylene <br /> dibromide(EDB) by EPA Method 8020 and for total lead by EPA Method 7420 <br /> Elevated concentrations of TPH and BTEX were detected in the samples collected from beneath <br /> Tank#1, Tank#2 and the product line No detectable concentrations of TPH or BTEX were found <br /> in the samples collected beneath Tank #3 or Tank #4 No detectable concentrations of EDB were <br /> found in any sample Total lead concentrations appear to be within the range of naturally occurring, <br /> background concentrations Analytical data are summarized in Table 1 UST and soil sample <br /> locations are depicted on Figure 2 <br /> The generally good condition of Tank#2 and the lack of significant odor and discoloration noted by <br /> the inspector above a depth of 11 feet suggests that the primary source of contamination at the site <br /> may have been the adjacent Tank #1 which was noted to have holes Fill and native soil within the <br /> Tank #1 excavation were described as having "severe" odor and discoloration from the surface to <br /> the sampling depth of 10 feet <br /> data\grounzelhwTyslsumrpt doe <br />