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. TABLE 1 <br />' GROUNDWATER ELEVATIONS* <br /> Geweke Land Development & Marketing <br /> 16 South Cherokee Lane, Lodi, California <br /> ICasing Depth To Groundwater Elevation <br /> Well I D Elevation Groundwater (MSL) <br />' (MSL) 3194 6/94 3/94 6/94 <br /> EW-1 5321 5784 5956 -453 -635 <br /> MW-1 5374 57 84 DRY -4 10' DRY <br />' MW-2 5408 5758 DRY -3 50t DRY <br /> MW-3 5376 5828 DRY -452 DRY <br /> MW-4 5403 5807 DRY -4 04t DRY <br /> MW-5 5392 5808 DRY -4 16' DRY <br />' MW-6 5299 5709 5868 -410 -569 <br /> MW-7 5390 5853 6031 -463 -641 <br /> MW-8 5368 5830 6007 -462 -653 <br /> MW_9 5354 5829 5991 -475 -637 <br /> MW-10 5321 5753 5912 -432 -5 91 <br /> MW-11 5295 5794 5953 -499 -658 <br /> MW-12 5335 5890 6042 -555 -707 <br />' MW-13 5336 5895 6077 -559 -741 <br /> MW-14 5382 5816 5997 -4 34 -6 15 <br /> 70 easurements rn Feet <br /> Due to lack of recharge,measured groundwater depths are not representative <br /> were transported in a chilled container to McCambell Analytical in Pacheco (MAI) The <br /> Isamples were analyzed for total petroleum hydrocarbons (TPH as gasoline), volatile <br /> aromatics (BTE&X), volatile halocarbons, Iead (Pb) and ethylene dibromide (EDB) in <br /> accordance with EPA methods 8015m, 602, 601, 7420 (239 2) and 601, respectively <br /> On June 22, 1994, two groundwater samples were collected from EW-1 and MW-14 These <br /> samples were transported under chain-of-custody procedure to Alpha Analytical <br /> Laboratories (AAL) in Ukiah and analyzed for fecal coliform <br /> L.33f6941GL 3M QM4 7 <br />