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rrealagko,rechn!"Inc Page 8 <br /> Groundwater Monitoring Report <br /> Project No 723 2 <br /> October 25,2005 <br /> 2 MTBE <br /> • None of the wells sampled contained MTBE above the laboratory reporting limits and <br /> ' therefore contour diagrams were not produced EPA Method 8260B was utilized for <br /> this event <br /> • MTBE does not appear 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 northwest and southwest locations of <br /> wells MW-7 and MW-9, respectively Well MW-8 historically has less benzene than <br /> MW-5 also <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 west, northwest, northeast and <br /> southwest locations of wells MW-1, MW-107, MW-108 &MW-109, respectively <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 northwest and southwest locations of wells MW-207 & MW-209, respectively <br /> 1 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 However, this trend may be reversed <br /> by the higher than average precipitation experienced this spring of 2005 <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 deepest well MW-101 intermittently contains BTEX contaminants and it <br /> contained low levels TPH-G for the event The TPH-G concentrations in MW-101 have <br /> exhibited a slight increasing trend since March 2004 <br /> ❑ Deep well MW-201 occasionally contains trace BTEX but was non-detect for the third <br /> consecutive event The intermittent contamination is probably a drilling artifact created <br /> by the use of mud rotary drilling The contaminant concentration decline since the first <br /> ' monitoring event in December 2001 supports the conclusion that the initial high <br /> concentrations were from a drilling artifact <br /> ❑ 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 /> between the water table and the TPH-G concentrations Benzene concentrations have <br /> stabilized in the well <br /> ' ❑ Figure 11 illustrates TPH-G and Benzene concentrations versus elevation in well MW-4, <br /> which lies up gradient of the core of the plume The contaminant concentrations exhibit a <br /> decreasing trend in this well <br /> 1 <br />