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' 3.ANNUAL REPORT FOR 2014 <br /> groundwater was no longer being pulled into the capture zone (and into wells N-16 and <br /> N-17) to dilute the BTEX and TPH constituents that were being pulled downgradient from <br /> the source area. Since the initial concentration increases after the extraction was shut down, <br /> ' a new equilibrium appears to have been established where the naturally occurring processes <br /> are resulting in decreasing concentrations for the BTEX and TPH constituents. <br /> 3.2 Effectiveness of the Current Remediation System <br /> The current remediation system consists of MNA and the phytoremediation system,as <br /> ' summarized in Section 1. The combination of these two strategies is effective,resulting in a <br /> sitewide decline in TPH and BTEX concentrations in groundwater and a stable-to-shrinking <br /> extent of these constituents in groundwater. As discussed with the RWQCB during <br /> ' meetings on July 12,2007, and September 21,2007, and reflected in the current MRP issued <br /> by the RWQCB,the steady reduction in hydrocarbon mass, as well as reductions in BTEX <br /> and TPH concentrations,at the Site are the result of fate-and-transport processes occurring <br /> naturally in the subsurface. These naturally occurring processes are documented in the Final <br /> Site Characterization Report(CH2M HILL,2002) and in the 3-Year Evaluation of the <br /> Bioremediation Pilot Study (CH2M HILL,2007a). The steady reduction in hydrocarbon mass <br /> is shown in the time-series concentration charts in Appendix D and Appendix E. <br /> 3.3 Identification of Data Gaps and Potential Deficiencies/ <br /> 1 Redundancies <br /> No data gaps or deficiencies have been identified. Routine groundwater monitoring at the <br /> ' Site was implemented in March 1992. To date,the groundwater monitoring program has <br /> been performed for approximately 24 years and has provided important time-series <br /> information with respect to groundwater elevations and gradients,NAPH thicknesses, and <br /> chemical concentrations in groundwater and surface water. Seasonal patterns in <br /> groundwater elevation fluctuations, as well as seasonal and long-term trends in BTEX and <br /> TPH concentrations,have been identified,as documented in the Final Site Characterization <br /> Report (CH2M HILL,2002) and in subsequent routine groundwater monitoring reports. <br /> Robust data have been collected to demonstrate that the naturally occurring processes are <br /> sufficient to result in a continued declining trend of these hydrocarbon constituents without <br /> the active remediation systems,as documented in the 3-Year Evaluation of the Bioremediation <br /> Pilot Study(CH2M HILL, 2007a). <br /> Current MRP No. R5-2007-0831 was developed to be streamlined to monitor current Site <br /> conditions with MNA and phytoremediation as remedies. This MRP eliminated most of the <br /> parameters added in the previous MRP to monitor the bioremediation pilot test,eliminated <br /> 1 unnecessary monitoring wells and parameters, allowed for the destruction of unnecessary <br /> monitoring wells, and allowed for the destruction of the soil vapor extraction well system. <br /> HydraSleeve samplers are now used to collect groundwater samples as approved in a <br /> November 10,2011, email from the RWQCB to SFPP. This"no purge" sampling <br /> methodology was implemented on a sitewide basis beginning with the first semiannual <br /> ' 2012 sampling event. A study was performed during the second semiannual 2011 sampling <br /> event that included split sampling for 50 percent(7 of 14) of the wells,using both <br /> methodologies,which captured the range of conditions at the Site (low-to-high <br /> ES101214202053SCO 3-3 <br />