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Fox River Paper Company January 31,2007 <br /> Combined Annual and 4th-Quarter 2006 Groundwater Monitoring Report Page 8 of 9 <br /> Conclusions <br /> • The application of plant-process water for the irrigation of tree orchards and the potential <br /> infiltration from the process-water ponds and aeration basins, is thought to have caused <br /> groundwater mounding in the semiperched, upper, and intermediate aquifers (Figures 6, 7 and <br /> 8). Infiltration of plant process water is suspected to be responsible for the elevated <br /> conductivity levels measured in the semiperched aquifer(Figure 9). The sources of the <br /> elevated conductivity measured along the northern boundary of the property in the <br /> semiperched and upper aquifers are unknown at this time(Figures 9 and 10). <br /> Recommendations <br /> It is recommended that the CVRWQCB reduce the monitoring frequency at this site from <br /> quarterly to semiannual (once during the wet season and once during the dry season). This <br /> recommendation is based on previous analyses which indicate that groundwater quality <br /> beneath the site is relatively stable or only changing slowly through time as documented by <br /> fourteen years of quarterly groundwater-monitoring data. <br /> FR should begin the first phase of remedial action for the site, the importation and spreading <br /> of low TDS irrigation water in the east percolation field, during the 2007 irrigation season. <br /> Summary of work performed <br /> Depth to groundwater <br /> The depth to groundwater was measured in all wells prior to purging and sampling using an <br /> • Actat Model 300 electric well probe. The depth to groundwater was recorded to the nearest <br /> 0.01 foot(Table 4). <br /> Purging procedures <br /> All wells (except wells PW-4, PW-5, PW-6, PW-7, and PW-8, which have dedicated <br /> submersible pumps)were purged using either a submersible Grundfos MPI 2-inch pump or an <br /> Enviro-Tech ES-60 1.875-inch PVC pump set up to 20 feet below the surface of the <br /> groundwater. Prior to sampling, each well was purged of three casing volumes of water or <br /> until field parameters stabilized. Purged water from wells TH-7 through TH-10 and wells M- <br /> 7-A, M-11-A, M-11-C, and M-19-C were transported to Nestles' water treatment system in <br /> Ripon for disposal because TCE or various TCE daughter products have been detected in <br /> these wells. Purged water from all other wells was disposed by direct discharge to the ground <br /> surface and allowed to infiltrate/evaporate. <br /> Sample collection <br /> Groundwater samples were collected directly from the discharge pipe from the submersible <br /> pump. The samples were stored on ice in a cooler, and delivered under chain-of-custody to <br /> BC Laboratories, Inc. in Bakersfield, California for analyses. <br /> Field analyses <br /> Field analyses for temperature, conductivity, and pH were performed on groundwater samples <br /> using a Cole-Parmer portable pH/conductivity meter (model number 19825-00). Turbidity <br /> measurements were performed on groundwater samples using a Cole-Parmer turbidimeter <br /> • (model number A391-50; Table 4). <br /> 005194.00, Task 8 Lawrence&Associates <br /> W:IC(ientsIFoxRiverlQuarter[yMonitoring1200614Q200614th 2006reportdoc <br />