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J/�COB5 Second Semiannual and 2018 Annual Groundwater Monitoring Report <br /> 3.1.2 Nonaqueous-Phase Hydrocarbons <br /> NAPH was not detected in any of the groundwater monitoring wells in 2018. NAPH has not been detected • <br /> at the site since 2002. <br /> 3.1.3 Total Petroleum Hydrocarbons and Benzene, Toluene, Ethylbenzene, and Total Xylenes • <br /> TPH and BTEX constituents were not detected in shallow downgradient wells M-8, N-19, and N-20 during <br /> this semiannual event, which is consistent with historical monitoring results. TPH and BTEX constituents <br /> also were not detected in the deeper well (N-24) during the first and second semiannual events in 2018. <br /> TPH and BTEX constituents were not detected in well N-18, except for the periodic detections of benzene • <br /> in the past several years at low concentrations and a detection of total xylenes in the 2017 second • <br /> semiannual monitoring event. The previous detections of benzene have occurred since 2010, which is <br /> consistent with the construction and use of farm buildings in the immediate vicinity of this well. A shallow <br /> seep has been observed near N-18 during this time, which could have been from the building septic <br /> system. <br /> TPH and BTEX constituents continue to be detected in the remaining monitoring wells, which are located <br /> in the former release area (N-7 and N-15), on the plume fringe (0-1, N-8, and N-16), and in the former <br /> extraction wells (RW-1 and N-17). As shown in the time series concentration charts in Appendix D, since <br /> the start of the bioremediation pilot test, the long-term TPH and BTEX concentration trends have <br /> continued to decrease for the wells with lower concentrations located on the plume fringe (0-1, M-10, <br /> and N-8) and for the wells with higher concentrations located in the former release (source) area <br /> (N-7 and N-15). • <br /> All of these wells historically had NAPH, which is no longer detectable. The long-term concentrations for <br /> former extraction well RW-1 have exhibited a decreasing trend since monitoring of this well began • <br /> in 2005. The decreases in wells M-10 and 0-1 have occurred to such an extent that they are almost no <br /> longer in the hydrocarbon plume. Before the start of the bioremediation pilot test, no long-term TPH and <br /> BTEX concentration 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 areas of higher <br /> contamination near the source area, which sustained the hydrocarbon concentrations. Since the start of <br /> the bioremediation pilot test in February 2004, the concentrations in wells N-16 and N-17 have shown <br /> similar behaviors, as described in the following paragraph. <br /> Overall, the concentrations of TPH and BTEX constituents began to increase after extraction stopped <br /> from well N-17 in February 2004. This likely occurred because clean, downgradient groundwater was no <br /> longer being pulled into the capture zone (and into wells N-16 and N-17) to dilute the TPH and BTEX <br /> constituents that were being pulled downgradient from the source area. Since the initial concentration <br /> increases after the extraction was shut down, a new equilibrium appears to have been established <br /> wherein the naturally occurring processes are resulting in decreasing concentrations for the TPH and <br /> BTEX constituents. <br /> 3.2 Effectiveness of the Current Remediation System • <br /> The current remediation system consists of MNA and the phytoremediation system, as summarized in <br /> Section 1. The combination of these two strategies is effective, resulting in a sitewide decline in TPH and • <br /> BTEX concentrations in groundwater, and a stable-to-shrinking extent of these constituents in <br /> groundwater. <br /> As discussed with the RWQCB during meetings on July 12, 2007, and September 21, 2007, and reflected <br /> in the current MRP issued by the RWQCB, the steady reduction in hydrocarbon mass, as well as , <br /> reductions in TPH and BTEX concentrations, at the site are the result of fate-and-transport processes <br /> occurring naturally in the subsurface. These naturally occurring processes are documented in the Final <br /> Site Characterization Report(CH2M, 2002) and in the 3-Year Evaluation of the Bioremediation Pilot • <br /> AX 1015181035SCO • <br /> • <br />