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r <br /> i <br /> U.A "OYU, 47K-91704:1 I,! <br /> Tow A <br /> Fes'+ <br /> Quarterly Ground-Water Monitoring <br /> March 8, 1989 <br /> Beacon Station No. 3-492, Manteca, California AGS 86102-3 <br /> were also collected, but were not analyzed. A Chain of Custody <br /> Record was initiated by the field geologist and accompanied the <br /> samples to the analytical laboratory. A copy of that record is <br /> attached to this letter report. <br /> On the dates free product was present in well MW-1, it was <br /> removed by bailing. The free product and purge water was <br /> temporarily stored onsite in 55-gallon, labeled 17-E drums <br /> approved by the Department of Transportation pending removal by <br /> Beacon to their refinery in Hanford, California, and subsequent <br /> treatment in a waste water separator. <br /> The samples collected from monitoring wells MW-2 and MW-3 were <br /> analyzed at Applied GeoSystems' laboratory in Fremont, California <br /> (California Hazardous Waste Testing Laboratory Certificate No. <br /> 153) , for total petroleum hydrocarbons (TPH) as gasoline by <br /> '.� modified Environmental Protection Agency (EPA) Method 8015 and <br /> the purgeable gasoline constituents benzene, toluene, <br /> ethylbenzene, and total xylene isomers (BTEX) by EPA Method 8020. <br /> The results of these and previous results are summarized in <br /> Table 2, and indicate that the benzene concentration in the <br /> r. sample from well MW-2 was above the action levels for drinking <br /> ?r water recommended by the California Department of Health Services <br /> (DHS) . The concentrations of toluene, ethylbenzene, and total <br /> xylene isomers in the sample from well MW-2 were below the <br /> detection limits or below the recommended action levels. TPH and <br /> BTEX concentrations in the sample from well MW-3 were below the <br /> detection limits of the methods used. Copies of the laboratory <br /> Analysis. Reports are attached to this letter report. <br /> The ground-water gradient across the site was evaluated by <br /> combining measurements of the static water level with the <br /> relative elevation of the top of the casing in each monitoring <br /> well. The relative elevation of the top of the casing in each <br /> well was previously evaluated with a Lietz/Sokkisha Che Automatic <br /> r Level. The static water levels ::ere adjusted using the top of <br /> the casing in well MW-2 as a common datum. These data are <br /> summarized in Table 3, and were used to evaluate the gradient of <br /> the stat'_c ground-water surface. On the dates the measurements <br /> were taken the maximum difference in the depth to the ground-- <br /> _;.� water surface in the three wells was evaluated to be less than <br /> 0.03 foot, which is within the instrument error over a distance <br /> of 75 feet. The ground-water gradient is, therefore, considered <br /> flat; similar results have been obtained during previous <br /> .._.______gradient.._evaluatigns___The ground-water gradient evaluations diva <br /> -.. the-pr _...... _... product in <br /> not include corrections for �esence of floating <br /> well MW-1. <br /> 3 <br /> ,4jOp/1490 GOOSStOMS <br />