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Report; Groundwater-quality Monitoring—April 15,2003: 7500 West Eleventh Street, Tracy, CA. Page 6 <br /> ,. .,� 2.0 APRIL 15, 2003 GROUNDWATER SAMPLING AND ANALYSIS <br /> On April 15, 2003, the tenth round of groundwater-quality monitoring was conducted. <br /> Monitoring Wells MW-1 through MW-3,MW-3A, MW-3B, MW-4 through MW-12, and <br /> MW-12A, which are at the locations shown on Figure 2, were sampled. <br /> i. <br /> '- 2.1 Groundwater Elevations and Flow Direction <br /> To initiate the April 15, 2003 sampling program, the depth to groundwater in each of the <br /> �:_j fifteen monitoring wells was measured using a conductivity probe. The water table <br /> elevations were computed relative to mean sea level (MSL). Those measurements and <br /> j the computed groundwater table elevations are recorded in Table 1, <br /> i In the period from January 20, 2003, the date on which the depths to groundwater in the <br /> monitoring wells were last measured, to April 15, 2003, the groundwater table rose <br /> between 0.04 ft. and 0.54 ft in the groundwater-quality monitoring wells. This is " <br /> consistent with the seasonal patter of agricultural irrigation that dominates groundwater <br /> =� levels in the area around Tracy. <br /> When crops are being irrigated, very large volumes of water are imported to the fields <br /> around Tracy via the Delta-Mendota canal, and water pumped from deep agricultural <br /> wells is being discharged to shallow aquifers. This activity begins in the spring of each <br /> year and typically continues through early- to mid-September, when it stops and <br /> ' J1> groundwater levels in shallow aquifers begin to fall. Except in unusually wet winters, <br /> levels continue to fall until some time in February or March. Inspection of Table 1 shows <br /> i that the rises and falls in the groundwater table elevation beneath the 7500 West Eleventh <br /> Street site usually occur with little or no relationship to seasonal precipitation in the San <br /> Joaquin Valley. <br /> The groundwater elevations presented in Table 1 were used to generate the groundwater <br /> contours shown on Figure 2. However, because, as is noted in Table 2, an apparent 0.52 <br /> ft. of floating product was detected in Monitoring Well MW-7, the groundwater elevation <br /> :Y in that well was corrected for the purpose of drawing the groundwater contours to allow <br /> for the depression of the water table in the vicinity of that well by the hydrocarbon fuel <br /> products floating on the surface of the water. The correction was derived as follows: <br /> Assume Specific Gravity of Diesel=0.84 <br /> ` a <br /> Assume Specific Gravity of Gasoline=0.74 <br /> I Assume relative proportions of diesel and gasoline in the floating product in Monitoring <br /> Well MW-7 are in the same ratio as the concentrations of diesel and gasoline in the <br /> sample of groundwater recovered from that well on December 13, 2001. They were, <br /> respectively, 500,000 µg/L and 61,000 µg/L. (See Table 2.) <br /> Thus, the estimated specific gravity of the floating product in well MW-7 is: <br /> sic <br />