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I <br /> It ' <br /> I <br /> ., 26 April 2004' <br /> AGE-NC Project No 97-0333 <br /> Page 11 of 12 <br /> ' s <br /> The results from the ground water monitoring and sampling events performed in August 2003 are <br /> as follows <br /> • Generally, depth to ground water at the site varied between 24 and 26 feet bsg,ground water <br /> elevations ranged between 6 46 feet(MW-9E) and 7 95 feet (MW-4) above mean sea level <br /> The ground water elevation increased approximately'0 68 feet between August 2003 and the <br /> November 2003 ground water monitoring events, the average increase in may be due to <br /> seasonal fluctuation, however, the ground water elevation is the lowest documented at the <br /> site <br /> ' First Zone ground water flow was inferred to be towards a ground water depression in the <br /> area of wells EW-1,MW-2,MW-6 and MW-7A at a gradient between 0 003 ft/ft and 0 008 <br /> ft/ft (Figure 4) <br /> ' Second Zone,Third Zone and Pnmary Aquifer ground water flow was inferred to be towards <br /> the south-southwest and south-southeast at approximate gradients of 0'001 ft/ft or less <br /> (Figures 5, 6 and 7, respectively) <br /> • Due to` the low ground water gradient at the site, small variations in ground water! <br /> measurements or changes of recharge/discharge of the local ground water could greatly <br /> modify the inferred ground water flow direction <br /> • The highest on-site concentrations of dissolved MTBE were detected in the samples <br /> collected in the area of First Zone monitoring wells MW-2, MW-6 and MW-7A at <br /> ' concentrations as high as 28,000µg/1 Lower concentrations of on-site MTBE were detected <br /> I ' <br /> in water samples from First,Second,Third and Primary Aquifer Zone monitoring wells MW- <br /> ' ;I 1, MW-3, MW-7 (B-E) and MW-8 (A and C), generally, moderate to significant MTBE f <br /> increases were reported this quarter from most of the on-site wells(Figures 8 and 9,Table 3) <br /> • <br /> Off-site MTBE was reported only in the water sample from Second Zone monitoring well <br /> MW-1213 at a concentration of 30 µg11 <br /> I I <br /> • Concentrations of PCE and/or TCE have been detected in water samples collected from all <br /> ' well locations associated with the Rainwater Car Wash investigation Minor to significant <br /> PCE and)or TCE concentrations were detected in 39 of 47 ground water monitoring wells <br /> located in First Zone, Second Zone,Third Zone and Primary Aquifer Zone Aquifers (Figure <br /> ' '10, Table 4) The highest concentrations of dissolved PCE were detected in the samples <br /> collected in the area of on-site well MW-10B(upper Second Zone),and offsite well MW-12A <br /> (First Zone) at concentrations as high as 1,400 µg/1 <br /> ' I <br /> I i • PCE and TCE are chlorinated solvents often associated;with dry cleaning operations Based <br /> on a August 2003 PCE iso-concentration map I iii First Zone water (Figure 10), AGE <br /> ' finterpre'ts the PCE/TCE-plume to have originated from the dry cleaner's facility located I <br /> 'immediately east of the Rainwater Car Wash <br /> SII ' I ' ' f <br /> AdvaiseedGeoEnvironmental,Inc i <br /> t ,IC <br />