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CALIFORNIA REGIONAL WATER QUALITY CONTROL BOARD <br /> CENTRAL VALLEY REGION <br /> ORDER NO. <br /> WASTE DISCHARGE REQUIREMENTS <br /> FOR <br /> TRIPLE E PRODUCE CORPORATION <br /> GROUND WATER TREATMENT AND DISPOSAL FACILITIES <br /> SAN JOAQUIN COUNTY <br /> The California Regional Water Quality Control Board, Central Valley Region, (hereafter Board)finds <br /> that: <br /> 1. Triple E Produce Corporation (hereafter Discharger) submitted a Report of Waste Discharge <br /> (ROWD), dated 24 June 1995, and a site evaluation report, dated 12 July 1995. On 22 November <br /> 1995,Triple E Produce requested the ROWD be amended so that the ground water treatment and <br /> disposal waste discharge requirements (WDRs) be made separate from those for the industrial <br /> wastewater treatment and disposal operations. This Order will only be applicable to the <br /> Discharger's ground water treatment and disposal facilities. T <br /> 2. Triple E Produce Corporation operates a fresh market tomato packing facility that uses E <br /> chlorination for preparing tomatoes for market. The Triple E facility is on Linne Road, near the <br /> town of Carbona in the NW 1/4 of Section 10,T3S,RSE, MDB&M as shown in Attachment A, N <br /> which is attached hereto and part of the Order by reference. 1 <br /> 3. Ground water beneath the Dischargers' property is contaminated with trihalomethane (THM) T <br /> constituents resulting from the discharge of chlorinated tomato wastewater to infiltration pond. A <br /> The extent of the contaminated ground water goes from the Discharger's property to L� <br /> approximately 1500 feet north of Linne Road . The primary THM of concern is chloroform, a T <br /> byproduct of the Discharger's tomato preparation operations. T <br /> 4. Chloroform in the ground water has been historically as high as 1,900 µg/1 with a more recent I <br /> average (Mar 94 through Mar 95) of approximately 500µg/1. In an effort to lower the chloroform T <br /> concentrations in the ground water the Discharger has been using in-situ bioremediation V <br /> techniques since May 1993. The bioremediation technique has been some what successful, E <br /> however,it has not stopped the migration of the plume. <br /> 5. In an effort to control the migration of the chloroform plume in groundwater the Discharger has <br /> proposed to pump approximately 25 gpm of chloroform contaminated ground water from <br /> extraction wells and treat it through an aeration process at an existing aeration pond north of the <br /> Linne Road, as shown on Attachment B, which is attached hereto and part of this order by <br /> reference. <br /> 6. During the summer months when the evaporation rates are greatest, it is estimated that all but <br /> approximately 3 gpm of treated ground water will be either evaporated or percolated from the <br /> aeration pond. During the winter months it has been estimated that approximately 10 gpm will <br /> have to be disposed of in an alternative manner. Treated ground water that does not evaporate or <br /> percolate from the pond,will be pumped to the tomato wash water treatment plant for further <br /> treatment prior to being sprinkled onto sixteen acres of apricots adjacent the Discharger's tomato <br /> packing facilities,see attachment B. <br /> 7. The extracted ground water will be aerated in the existing aeration pond to both strip the <br /> chloroform from it and to add oxygen so the water repercolating into the ground water will aid in <br /> the continued bioremediation efforts. <br /> 8. The site lies within the hydrologic unit/area/subarea No. 543.00, as depicted on interagency <br /> hydrologic maps prepared by the Department of Water Resources in August 1986. <br />