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WASTE DISCHARGE REQUIREMENTS ORDER R5-2012-0105 9 <br /> DIAMOND PET FOOD PROCESSORS OF RIPON, LLC AND <br /> RIPON COGENERATION, LLC <br /> DIAMOND PET FOOD RIPON FACILITY <br /> SAN JOAQUIN COUNTY <br /> located along the western property boundary near the City of Ripon's WWTF. The area <br /> of lowest TDS (background well OB-17)was in the southeastern comer of the site along <br /> the Stanislaus River. <br /> The average EC and TDS concentrations in all shallow zone wells except Well OB-17 are <br /> greater than the recommended Secondary Maximum Contaminant Levels (MCLS) of <br /> 900 pmhoslcm for EC and 500 mglL for TDS, respectively. The elevated TDS levels in <br /> the northeastern quadrant of the site are likely caused by the eucalyptus trees' <br /> concentrating effect on TDS. The elevated TDS levels observed along the western <br /> portion of the site, particularly in the southwest corner, probably reflect the infiltration of <br /> higher TDS water originating at the City of Ripon's WWTF encroaching onto the Diamond <br /> site. <br /> 39. After the paper mill was closed in May 2009, Ripon Cogeneration, LLC continued to <br /> discharge and dilute the discharge with lower salinity fresh water. Since then, the <br /> groundwater TDS concentrations in wells OB-2, OB-08, OB-10, OB-18, OB-19 and OB-20 <br /> have slightly decreased. However, the TDS concentrations in other shallow zone wells <br /> have not changed significantly. <br /> 40. The predicted wastewater TDS concentration of 684 mglL is less than the TDS <br /> concentrations in the shallow zone groundwater monitoring wells at the site, except for the <br /> wells near the river(Wells OB-17 and OB-22). Based on the projected effluent quality, the <br /> method of disposal and existing groundwater quality, it is unlikely that the proposed <br /> discharge will significantly degrade the groundwater quality for TDS. <br /> 41. The groundwater monitoring network should be designed to yield samples representative <br /> of the upper most portion of the first aquifer underlying the site. Therefore, this Order <br /> requires the Dischargers to monitor certain monitoring wells in the first aquifer zone. <br /> Those unused monitoring wells, which are not required to be monitored in this Order and <br /> are not monitored by Nestle for remediation, can be destroyed with the approval of the <br /> Central Valley Water Board. This Order requires the Dischargers to submit a <br /> Groundwater Monitoring Well Destruction Plan. <br /> Basin Plan, Beneficial Uses, and Regulatory Considerations <br /> 42. The Water Quality Control Plan for the Sacramento River and San Joaquin River Basins, <br /> Fourth Edition (hereafter"Basin Plan") designates beneficial uses, establishes water <br /> quality objectives, contains implementation plans and policies for protecting waters of the <br /> basin, and incorporates by reference plans and policies adopted by the State Board. <br /> Pursuant to Water Code section 13263(a), waste discharge requirements must implement <br /> the Basin Plan. <br /> 43. The site is immediately adjacent to the Stanislaus River, which is the southern property <br /> boundary of the facility. Local drainage is to the Stanislaus River. The designated <br /> beneficial uses of the Stanislaus River, as specified in the Basin Plan, are municipal and <br /> domestic supply; agricultural supply; industrial process and service supply; hydropower <br /> generation; water contact recreation; non-contact water recreation; warm and cold fresh <br /> water habitat; cold water migration of aquatic organisms; spawning, reproduction, and for <br /> early development; and wildlife habitat. <br />