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Neenah Paper,Inc. July 27,2010 <br /> First-Half 2010 Groundwater-Monitoring Report Page 3 of 7 <br /> irrigation water had the additional benefit of creating a hydrologic barrier between ASB-2's <br /> TDS plume and the production wells. Improving the quality of water in the vicinity of the <br /> production wells ultimately improves the quality of water discharged by the mill as effluent. <br /> According to L&A's groundwater model, the infiltration of 67 acre feet of water annually to the <br /> east percolation field, over a five year period, will bring TDS levels in the semiperched and <br /> upper aquifers into compliance with the site's WQPS. <br /> Groundwater quality improved in the immediate vicinity of the east percolation field in the <br /> semiperched, upper, and intermediate aquifers following the application of SSJID water.3 <br /> The third season of applying low TDS water to the east percolation field began on August 3, <br /> 2009, and ended on September 23, 2009. A total of 21.77 acre feet (7.1 million gallons) of <br /> water from production well PW-6 were placed on NP's east percolation field. <br /> First-Half 2010 Groundwater Monitoring <br /> Findings, first-quarter 2010 <br /> First-quarter 2010 groundwater levels were measured on January 11, 2010, and are presented in <br /> Table 3 (following text). <br /> Mounding was present within the semiperched aquifer in the vicinity of wells OB-9 and OB-18. <br /> The direction of the semiperched gradient was away from the mound then generally towards the <br /> northwest at magnitudes ranging between 0.002 and 0.00084 feet/foot (ft/ft; Figure 3). <br /> Mounding was present within the upper aquifer in the central and southeast corner of the site. <br /> The direction of the gradient was away from the mound then generally towards the northwest at <br /> magnitudes ranging between 0.001 and 0.00094 ft/ft(Figure 4). <br /> Mounding was present within the intermediate aquifer north of the City of Ripon MWWTF and <br /> in the vicinity of Neenah monitoring well TH-11; additionally, the influence of production well <br /> PW-6 was evident from the depression of the groundwater gradient in the southeastern corner of <br /> the site as well as the Nestles' extraction system on Stockton Avenue. The magnitude of the <br /> gradient ranged between 0.002 and 0.0027 ft/ft(Figure 5). <br /> Findings, second-quarter 2010 <br /> Second-quarter 2010 groundwater elevations were measured on April 5, 2010, and groundwater <br /> samples were collected between April 6 and 7, 2010. Field and laboratory results are presented <br /> in Table 4 (following text). <br /> The direction of the semiperched aquifer groundwater gradient was generally towards the <br /> northwest at a magnitude of 0.0013 ft/ft(Figure 6). <br /> The direction of the upper aquifer groundwater gradient on April 5 was generally towards the <br /> northwest at a magnitude of 0.0011 ft/ft(Figure 7). <br /> The direction of the intermediate aquifer groundwater gradient was generally towards the <br /> northwest at magnitudes ranging between 0.00032 and 0.00043 ft/ft(Figure 8). <br /> The areas of highest Specific Conductance (SC) in the semiperched aquifer were in the <br /> northeast quadrant of the NP site in well OB-4 (2,438 µmhos/cm), along the northwestern <br /> property boundary in the City of Ripon's monitoring well MW-7 (2,038 µmhos/cm), adjacent to <br /> 3 L&A,February 8,2008, Combined 2007 Annual Summary Report, 4th-Quarter 2007 Groundwater-Monitoring <br /> Report,And Preliminary Corrective Action Evaluation,Neenah Paper Company,Ripon, California. <br /> 005194.04 Task 4 Lawrence&Associates <br /> W.•I CLIENTSIFoxRiver-NeenahlQuarterlyMonitoringl201011st half 2010 reporkdoc <br />