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' Gealo f Tec/uucs Inc. Page 7 <br /> Groundwater Motutonng Report <br /> Project No 724 2 <br /> November 12,2004 <br /> ' conditions We acknowledge that there may be undiscovered conditions, which would upon <br /> their consideration, change our interpretation and thus our conclusions <br /> ' Our recommendations are based on our knowledge of site conditions, and on the state and <br /> limitations of subsurface investigative technology <br /> ' Conclusions <br /> • This report details the third sampling event of the nine new wells installed in <br /> December 2003 and the existing ten wells The groundwater plume does not display a <br /> typical "core" but exhibits wide variations in contaminant concentration in both <br /> vertical and lateral planes as shown in Figures 6 - 12 The highest MTBE <br /> concentrations detected in the shallow, intermediate and deep aquifer were in wells 7 s,�6j-"7 <br /> MW-7 (2 9 µg/l), MW-106 (15 9 µg11) and MW-209 (7 0 µg/l), respectively These J <br /> wells are in line from the former UST and dispenser locations areas to the east in the <br /> ' predominant groundwater direction In addition, the highest TPH-G concentrations <br /> were detected to the east of the site in wells MW-106 and MW-208, and the highest <br /> Benzene concentrations were detected to the east and northeast in wells MW-106 and <br /> ' MW-108, respectively <br /> • In its correspondence dated September 3, 2002, the San Joaquin County <br /> (P� o Environmental Health Department (SJC/EHD) identified two LUFT sites (701 and <br /> � ��, 749 E Charter Way) up gradient of the subject site The contamination detected in <br /> yes �xr L the MW-108/208 location may be from an offsite source The rationale for this <br /> z v Z conclusion is that the TPH-G contaminant found m this well does not corroborate <br /> ' with the MTBE plume that seems to be migrating down gradient in an east-southeast <br /> direction, not in an east-northeasterly direction <br /> ' • The SJC/EHD also stated in their above letter that a sandy interval at 70 — 80 bgs <br /> could be acting as lateral conduit for contaminant migration ' The presence of <br /> contamination in deep wells MW-208 and MW-209 support this theory, however GTI <br /> ' still suggests that the levels do not warrant an engineered clean up <br /> • The trace Toluene previously detected in well MW-11 indicates that an up gradient <br /> source has contributed to the plume beneath the subject site Additional monitoring is <br /> ' R needed to confirm this possibility <br /> • The data shows that a relatively stable, wide spread, low concentration plume of <br /> petroleum hydrocarbon compounds are present in the groundwater at this site The <br /> ' deeper TPH-G plume is not defined to the north and the deeper MTBE plume is not <br /> defined to the east <br /> ' Recommendations <br /> • Maintain the current quarterly monitoring schedule to determine contaminant and <br /> ' gradient trends <br /> • Reduce the sampling frequency of the stable wells to a semi-annual basis to achieve <br /> project cost savings (MW-1, MW-3, MW-4, MW-5, MW-6 and MW-104) <br /> � 4 <br /> c <br />