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3.ANNUAL REPORT FOR 2013 , <br /> As shown in Figure 3 of this report and Figure 3 in Appendix F, groundwater flow patterns ' <br /> were consistent for the March 12, 2013,and September 13, 2013, data. These groundwater <br /> flow patterns are also consistent with flow patterns from historical monitoring events before <br /> and after the active remediation systems (GWETS and SVETS) were shut down in February <br /> 2004 for the 3-year bioremediation pilot study. Groundwater flow is described in Section 2 <br /> above. <br /> 3.1.2 NAPH <br /> NAPH was not detected in any of the groundwater monitoring wells in 2013. NAPH has not , <br /> been detected at the site since 2002. <br /> 3.1.3 BTEX and TPH , <br /> Except for an anomalous detection of benzene at well N-18,BTEX and TPH constituents <br /> were not detected in the shallow upgradient monitoring well (M-1) or shallow <br /> downgradient wells (M-8, N-19, and N-20) during the first and second semiannual sampling <br /> events in 2013,which is consistent with the historical monitoring results. BTEX and TPH <br /> constituents also were not detected in the deeper well (N-24) during the first and second , <br /> semiannual events in 2013. <br /> Benzene was detected at a low concentration(1.9 µg/L) in well N-18 during the first <br /> semiannual event in 2013. The detection of benzene is considered anomalous because BTEX <br /> constituents historically have not been detected in this well before 2010. These recent <br /> detection of benzene and other BTEX constituents since 2010 may be attributed to offsite ' <br /> sources,which include farm buildings in the immediate vicinity of this well. Well N-18 is <br /> being monitored to further evaluate the concentrations. <br /> BTEX and TPH constituents continue to be detected in the remaining monitoring wells, , <br /> which are located in the former release area (wells N-7 and N-15), on the plume fringe <br /> (wells 0-1,N-8,and N-16), and in the former extraction wells (RW-1 and N-17). As shown in <br /> the time-series concentration charts in Appendix D, since the start of the bioremediation <br /> pilot test,the long-term BTEX and TPH concentration trends have continued to decrease <br /> significantly for the wells with lower concentrations located on the plume fringe (wells 0-1, <br /> M-10,and N-8) and for the wells with higher concentrations located in the former release ' <br /> (source) area (wells N-7 and N-15). <br /> All these wells historically had NAPH,which is no longer detectable. The long-term ' <br /> concentrations for former extraction well RW-1 have exhibited a decreasing trend since <br /> monitoring for this well began in 2005. The decreases in wells M-10 and 0-1 have occurred <br /> to such an extent that well 0-1 is almost no longer in the hydrocarbon plume and well M-10 ' <br /> is now almost outside the plume. <br /> Before the start of the bioremediation pilot test,no long-term BTEX and TPH concentration <br /> trends for extraction well N-17 and nearby monitoring well N-16 were apparent. This <br /> potentially was due to extraction at well N-17 pulling hydrocarbons downgradient from the <br /> areas of higher contamination near the source area,which sustained the hydrocarbon <br /> concentrations. Since the start of the bioremediation pilot test in February 2004,the <br /> concentrations in wells N-16 and N-17 have shown similar behavior. <br /> 3-2 WBG101513183707SCOMOLT 2SA13_REPORT_FINAL ' <br />