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Diamond Pet Food Processors of Ripon California LLC January 28, 2011 <br /> Combined Amoral and Fourth-Ouarter 2010 Groundwater Monitoring Report Page 6 of 8 <br /> Mann-Kendall Analysis <br /> Mann-Kendall Trend Analysis was perform for all analytes in all wells (Attachment B). Table <br /> 5 (following text) presents the results of the trend analyses at the 2% significance level. Trend <br /> analyses for TDS show more improvements in water quality in the southeastern part of the site, <br /> reflecting application of the higher quality surface or groundwater to the east percolation field. <br /> The trend analyses also show more degradation of groundwater quality in the northeastern part <br /> of the site,reflecting concentration of constituents from evapotranspiration by the eucalyptus <br /> trees,4 and in the southwestern part of the site from the inflow of high TDS water from the City <br /> of Ripon's MW WTF. <br /> Figure 16 presents contours of the percentages of analytes per well that have stable or <br /> decreasing (down) trends. <br /> Sludge Monitoring <br /> No sludge was produced at the mill during 2010, therefore, sludge monitoring was not <br /> performed. <br /> Corrective Action Evaluation and Implementation Schedule <br /> In order to meet the WQPS adopted by the CVRWQCB for the site (Table 1), DP predecessor <br /> Neenah Paper chose to import low TDS (total dissolved solids) South San Joaquin Irrigation <br /> District (SSJID) water as the preferred corrective action method for reducing TDS levels in <br /> Plant effluent water and groundwater beneath the site.5,6 <br /> The water was provided by the City of <br /> Ripon and piped from their holding pond located on the north side of their MWWTF ponds. <br /> Groundwater-quality modeling predicted that the application of low (<150 mg/L) TDS water in <br /> the east percolation field would improve (lower) TDS levels by 100 to 500 mg/L, depending on <br /> the location in the subsurface, over a five year time period. <br /> Between June 26 and August 16, 2007, approximately 135.6 acre feet (44 million gallons) of <br /> low (133 mg/L) TDS water were pumped into DP's east percolation field and allowed to <br /> infiltrate into the subsurface. The east percolation field is located between a high TDS plume <br /> originating from the bottom of ASB-2 and production wells PW-6 through PW-8. In addition to <br /> recharging the semiperched aquifer with low TDS water, the irrigation water had the additional <br /> benefit of creating a hydrologic barrier between ASB-2's TDS plume and the,production wells. <br /> Improving the quality of water in the vicinity of the production wells ultimately improves the <br /> quality of water discharged by the mill as effluent. According to L&A's groundwater model, the <br /> infiltration of 67 acre feet of water annually to the east percolation field, over a five year period, <br /> will bring TDS levels in the semiperched and upper aquifers into compliance with the site's <br /> 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.7 <br /> a L&A,November 17,2008,Five-Year Water Ovalin,Review Report. <br /> s L&A,June 15,2005,Amended Report of Haste Discharge For Disposal Of Plant Effluent Water. <br /> 6 L&A,March 31,2006,Addendum To Amended Report of YVaste Discharge For Disposal Of Platt Effluent Water. <br /> 'L&A,February 8,2008, Combined 2007 Annual Su nmay Report, 4th-Quarter 3007 Groundwater-Monitoring <br /> Report,And Preliminati,Corrective Action Evaluadon, Neenah Paper Compania, Ripon, California. <br /> 70107.01 Task 2 Lawrence&Associates <br /> R':ICLIENTSI Diamond Per Fotnlsi0/011/7.01-Grutuul water MouitoringlGromidiāœ“ater Mmiitoring1201012ud 114 f 2fll/llannual-2nd Half <br /> 2010 repomdoc <br />