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�. <br /> uista <br /> 1 <br /> Quarterly Monitoring Report June 1, 1989 <br /> Former UNOCAL station No. 2$59, Stockton, California AGS e 1, 12-2 <br /> 98 <br /> nondetectable in well �. ]-1, and that concentrations of these <br /> constituents had increased in a ground-water sample collected <br /> from monitoring well MW-2, and remained near initially detected <br /> concentrations in a ground-water sample collected from monitoring <br /> well M IW-3, <br /> At your request, a geologist from Applied GeoSystems was present <br /> onsite March 2 and 3, 1989, to collect ground-water samples from <br /> monitoring wells MW-1 through MW-3. The depth to the ground- <br /> water surface in each monitoring well was measured to the nearest <br /> 0.01--foot with a Solinst water-level indicator. The ground water <br /> was found to be approximately 1/2-foot shallower in the recent <br /> sampling event than previously measured. The water-level data, <br /> summarized in Table 1, were used to construct a Ground-Water <br /> Potentiometric Surface Map across the site (Plate P-3) . <br /> Evaluation of depth-to-water data collected on March 2, 1989, <br /> indicate that the direction of ground-water flow at the site is <br /> northeast. The evaluated direction of ground-water flow on <br /> June 6, 1988, and October 26, 1989, was also northeast. The <br /> average gradient at the time of measurement was 0.0021. This <br /> value is similar to the ground-water gradient evaluated during <br /> the sampling event of June 6, 1988, and less than the ground- <br /> water gradient evaluated from data collected on October 26, 1989. <br /> In June 1988 the average gradient was 0.0017; the average <br /> gradient in October 1988 was 0.0068. <br /> _.4 Ground-water samples were collected from near the air-fluid <br /> interface in the monitoring wells for subjective analysis by <br /> lowering approximately half'tFe length of a clean Teflon bailer <br /> past the interface. The bailer was then retrieved and the water <br /> sample was examined for floating product, sheen, and other <br /> subjective evidence of hydrocarbon contamination. No floating <br /> product, product sheen, or emulsion was noted in samples from the <br /> monitoring wells. The results of these subjective analyses are <br /> presented in Table 2. <br /> Approximately 3 well volumes (30 gallons) of ground water were <br /> purged from the wells using a submersible pump. Recharge to the <br /> t wells was relatively rapid. Ground-water samples for laboratory <br /> analysis were then collected from the monitoring wells by gently <br /> lowering a clean Teflon bailer past_the.--.air water.-....interface--to--a-----_..-____.-- --------------.._.-._..---._-- <br /> ----------- -- - -- --- ----point--immediately bel-ow--the top of the water column. The bailer <br /> was then recovered and the sample slowly transferred to <br /> laboratory-cleaned, 40-milliliter glass vials to which <br /> concentrated hydrochloric acid had been added as a preservative. <br /> -- 2 <br /> AVP114erl G'e0Systerms <br />