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dichloropropane,tetrachloroethene, 1,2,3-trichloropropane, methylene chloride, benzene, toluene <br /> and xylene detected during this monitoring event. <br /> In general,the groundwater plume size appears stable with relatively consistent analytical results <br /> over time. Concentration trends appear to be generally stable. Two wells in the interior of the <br /> plume (MW-3B and MW-4B) have historically experienced significant variability in carbon <br /> tetrachloride concentrations over time. However, MW-3B appears to be relatively stable since <br /> the fourth quarter 2003. <br /> MRP R5-2007-0826 now requires semi-annual monitoring for select inorganic parameters in the <br /> groundwater plume monitoring wells. During the 18 June 2008 sampling event wells wells MW- <br /> 3B, MW-9B and EW-11B were analyzed for chloride; while wells MW-3B MW-4B, MW-5B, <br /> MW-913, MW-IOB, and EW-11B were analyzed for nitrate. Concentrations for nitrate, which is <br /> not required by the MPR, but used to monitor aquifer conditions favorable to carbon <br /> tetrachloride reduction, ranged between 22 mg/L and 46 mg/L and chloride ranged between 94 <br /> mg/L and 120 mg/L. Changes in chloride conentrations over time will provide information on <br /> the reduction of carbon tetrachloride to chlorides. Dissolved iron was not detected in any of the <br /> three wells sampled during the June 2008 sampling event. Total organic carbon was not analyzed <br /> during this monitoring event. <br /> Results from the analysis of inorganic parameters are presented in Table 6. <br /> 3.2 Recirculation Pilot Study Results <br /> During the 5 May 2008 pre-startup monitoring event, potentiometric elevations for the <br /> intermediate wells varied from 9.20 to 9.76 ft below mean sea level. Based on the water level <br /> data collected on 05 May 2008 the groundwater flow direction is interpreted to be variable with a <br /> hydraulic mound near well MW-9B. This hydraulic mound has consistently occurred since well <br /> MW-9B was installed near the zero valent iron injections. <br /> Carbon tetrachloride and chloroform was detected in all six monitoring wells sampled; <br /> concentrations ranged from 120 ug/1 to 740 ug/1 for carbon tetrachloride, and 23 ug/I to 120 ug/1 <br /> for chloroform. There were also low levels (less than 15 µg/1) of 1,2-dichloroethane, 1,2- <br /> dichloropropane, tetrachloroethene, 1,2,3-trichloropropane, methylene chloride, benzene, <br /> toluene, ehtylbenzene and xylene detected during this monitoring event. <br /> Groundwater samples collected in May and June 2008 from wells MW-313, MW-4B, MW-5B, <br /> MW-9B MW-IOB and MW-13B were analyzed for chloride with concentrations ranging <br /> between 100 mg/L to 130 mg/L. Nitrate and dissolved iron were not analyzed in May 2008. <br /> Results from the analysis of inorganic parameters are presented in Table 5. <br /> The groundwater recirculation pilot study was started on 19 May 2008 utilizing paired <br /> groundwater extraction and injection wells EW-11B and IW-BH2A. Extraction well EW-11B is <br /> located in the northwestern portion of the site, while injection well IW-BH2A is located <br /> 9 <br />