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s <br /> WEISS ASSOCIAM VIA <br /> Jack Fiori <br /> 27 may 1987 11 <br /> representing 18 March water levels, shows a gradient somewhat more <br /> northeasterly than that of 30 January. <br /> TABLE 3. Water Level Data, San Joaquin Mosquito Abatement, Lodi Facility <br /> Top-of- 30 January 1987 _ 18 March 1987 <br /> Casing Depth to Water Depth to Water <br /> Elev. Water Elev. Water Elev. <br /> (ft above (DTH) (ft above (DTH) (ft above <br /> Well No. HSL) (ft) HSL) (ft) MSL) <br /> MW-1 54.11 38.21-• i5.90 <br /> MW-2 54.28 37.92' 16,36 37.91 16.37 <br /> V-3 54.03 38.50* 15.53 38.50 15.78 <br /> * - DTW measured prior to well development. <br /> CONCLUSIONS <br /> »- During Phases 1 and 3 of this project TFHC were detected at <br /> concentrations of up to 3,600 ppm in soil beneath the 1,000-gallon gasoline <br /> tank. The concentrations increased with depth down to 31 ft below ground <br /> surface but there was no evidence that either the gasoline tank or the weed <br /> oil tank or associated piping had leaked. It appears that these hydrocarbons <br /> constitute a slug of indeterminate origin and a finite areal extent below the <br /> excavated gasoline tank. The soil samples collected from borings drilled <br /> a. <br /> during Phase 2 and the soil samples collected during Phase 4 were all below <br /> detection limits. The soil and ground water analyzed during Phase 5 were also <br /> below dwtettion limits, indicating that this material is bound in the soil and <br /> has not migrated to the ground water table at this time. <br /> WA concludes that hydrocarbons are present in unsaturated soil down to <br /> 31 ft. At approximately 30 and 32 ft below ground surface there is a <br /> lower-permeability layer which may retard and alter the direction of the <br /> hydrocarbons' vertical- movement. Continued migration vertically downaaxd is <br /> probable in the future. <br />