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Cieotog&al recluucs Mc Page 7 <br /> Groundwater Momtonng Report <br /> 10 Project No 723 2 <br /> February 28,2005 <br /> ' • Figure 6 illustrates the distribution of TPH-G in the deep wells A localized high is <br /> centered in well MW-208 and the concentrations attenuate to non-detectable and low <br /> levels in the southwest and northwest locations of MW-209 &MW-207, respectively <br /> 2 MTBE <br /> • The MTBE concentrations were not confirmed utilizing EPA Method 8250 and <br /> ' therefore contour diagrams were not produced When Method 8260 is utilized the <br /> wells are non-detect for MTBE <br /> o MTBE appears not to be an issue at this site <br /> 3 Benzene <br /> • Figure 7 illustrates the distribution of Benzene in the shallow wells A localized high <br /> ' is centered in well MW-5 that attenuates to the southwest location of well MW-9 <br /> The plume typically attenuates to the north and east in the locations of MW-7 and <br /> MW-8 that were dry for the event <br /> + Figure 8 illustrates the distribution of Benzene in the intermediate wells A localized <br /> high is centered in well MW-3 that attenuates to the southwest, west and northwest <br /> locations of wells MW-109, MW-1 & MW-107, respectively The plume also <br /> attenuates to the east in the location of MW-108 <br /> • Figure 9 illustrates the distribution of Benzene in the deep wells A localized high is <br /> centered in well MW-208 and the concentrations attenuate to non-detectable levels in <br /> the southwest, west and northwest locations of MW-209, MW-101 & MW-207, <br /> respectively <br /> The results of the groundwater sample analysis show the following <br /> ❑ Review of the historic groundwater elevations show that groundwater levels experience <br /> seasonal fluctuations from the mid 1990s to spring 2000 but have been decreasing <br /> ' steadily with each seasonal cycle since spring 2000 <br /> ❑ The concentrations of BTEX and TPH-G continue to fluctuate in individual monitoring <br /> wells from one sampling event to the next However, there is a general trend of <br /> ' concentrations tracking the groundwater elevations <br /> ❑ The main mass of contaminants appears to have migrated to the depth of the intermediate <br /> ' well screen interval (43 to 70 ft bgs) <br /> ❑ On site deep well MW-101 intermittently contains contaminants and it contained low <br /> levels of BTEX and TPH-G for the event It is noted that the contaminant concentrations <br /> in MW-101 have continuously declined since it's installation in contrast to the shallow <br /> wells that do not show a similar contaminant decline <br /> ❑ Deep well MW-201 contained trace BTEX (0 4 — 10 ug/1) The contamination is <br /> probably a drilling artifact created by the use of mud rotary drilling The contaminant <br /> concentration decline since the first monitoring event in December 2001 supports the <br /> conclusion that the initial high concentrations were from a drilling artifact <br /> t ❑ Figure 10 illustrates TPH-G and Benzene concentrations versus elevation in well MW-3, <br /> which lies near the core of the plume There appears to be a fairly direct relationship <br />