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Nestle USA, Inc., Ripon, California March 31, 2011 <br /> 2010 Annual Report <br /> TCE <br /> • Concentrations of TCE above the laboratory reporting limit were present in 29 of 56 <br /> wells in 2010 (Table 3.1) ranging from 0.55 pg/L (well M-52B, January) to 340 pg/L (well <br /> M-10A, October). <br /> • The spatial distribution of TCE concentrations in the Upper Aquifer has remained <br /> consistent over the past five years, except for a slight increase in the extent of TCE to <br /> the northwest toward well M-1 OA in 2007, 2008, and 2010 (Figure 9). <br /> • An increase in TCE concentrations in well M-10A from 85 pg/L in the Second Quarter <br /> 2009 to 250 pg/L in the Third Quarter 2009 prompted a subsurface investigation to <br /> assess groundwater conditions and concentration trend S13,14 ECM concluded that a <br /> decline in groundwater extraction from the Industrial Avenue treatment system <br /> (extraction wells EI-1 and EW-1), and the influence of variations in the pumping at <br /> municipal well MW-4 most likely caused the increase in the concentration of TCE in M- <br /> 1 OA. <br /> • Stable TCE concentrations over time are observed in 27 Upper Aquifer monitoring wells. <br /> Occasional fluctuations observed in some wells are likely due to changes in groundwater <br /> flow direction. Most of these wells are located close to the WWTP (e.g. M-1 7A and M-44 <br /> A). <br /> • Decreasing TCE concentration trends are present in 24 monitoring wells. TCE <br /> concentrations in wells near the Site, such as M-1A and M-3A (Appendix C) showed <br /> significant decreases which are indicative of continued success of source mass removal <br /> by the On-Site extraction and treatment system. <br /> Cis-1,2-DCE <br /> • Concentrations of cis-1,2-DCE were present in 18 of the 56 Upper Aquifer wells <br /> monitored in 2010 ranging from 0.53 pg/L (well M-50A, April) to 36 pg/L (well M-9A, <br /> April). <br /> • Cis-1,2-DCE concentration trends in each well generally follow the TCE trend as <br /> summarized above, except M-1 B. <br /> • Relatively higher cis-1,2-DCE concentrations as compared to TCE concentrations were <br /> observed in wells located southwest of the Stockton Avenue extraction and treatment <br /> system and in the vicinity of the City of Ripon WWTP (Figure 6). The presence of <br /> higher cis-1,2-DCE concentrations infers continued intrinsic remediation through the <br /> reductive dechlorination process near the WWTP and other biodegradation processes <br /> in areas distal to the WWTP1e <br /> VC <br /> • Concentrations of VC were present in five of the 56 Upper Aquifer wells sampled in <br /> 2010, and ranged from 0.56 pg/L (M-32A, April) to 1.6 pg/L (M-23A, April). <br /> • The presence of VC in Upper Aquifer wells is limited to wells located near the City of <br /> Ripon WWTP, except well M-6A, demonstrating continued reductive dechlorination in <br /> the vicinity of WWTP. <br /> • The presence of VC in well M-6A is a result of the pumping histories of municipal well <br /> MW-6, which was screened across all three aquifers, and of the Regal Almond well, <br /> which was screened in the Upper Aquifer. <br /> 14 <br />