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TENTATIVE <br /> CALIFORNIA REGIONAL WATER QUALITY CONTROL BOARD <br /> CENTRAL VALLEY REGION <br /> ORDER NO. R5-2003-XXXX <br /> WASTE DISCHARGE REQUIREMENTS <br /> FOR <br /> SPX CORPORATION <br /> MARLEY COOLING TOWER COMPANY STOCKTON FACILITY <br /> IN SITU GROUNDWATER REMEDIATION PILOT STUDY <br /> SAN JOAQUIN COUNTY <br /> The California Regional Water Quality Control Board, Central Valley Region, (hereafter Regional <br /> Board) finds that: <br /> 1. The Marley Cooling Tower Company(MCTC), a wholly owned subsidiary of SPX Corporation <br /> (hereafter collectively referred to as Discharger) submitted a Report of Waste Discharge (RWD), <br /> dated 8 November 2001, for a pilot study to evaluate the potential for in-situ treatment of <br /> groundwater containing chromium. The Discharger also submitted a(a) Supplemental Pilot Study <br /> Work Plan for In Situ Chromium Reduction at The Marley Cooling Tower Facility dated 21 <br /> January 2003 that proposed changes to the RWD, and (b) additional supporting information dated <br /> 1 and 16 April, and 1 May 2003. <br /> 2. The Discharger owns and previously operated a cooling tower fabrication plant at 150 N. Sinclair <br /> Avenue in the East Stockton Area in San Joaquin County(site). As part of the fabrication <br /> operations, the Discharger operated a wood preservation process utilizing solutions containing <br /> copper, chromium and arsenic. Wood preserving was discontinued at the site in January 1991, <br /> however past operational practices left waste constituents in soils and groundwater underlying the <br /> site. Soils contain copper, chromium, and arsenic; groundwater contains elevated concentrations <br /> of chromium. <br /> 3. The project site is shown on Attachment A, a part of this Order. The site is in Section 32, T2N, <br /> R7E,MDB&M. The project site plan is shown on Attachment B, a part of this Order. <br /> 4. The objective of the pilot study is to evaluate the(a) efficacy of in-situ hexavalent chromium <br /> reduction using calcium polysulfide and ethanol injection, (b) assess the secondary impacts of in- <br /> situ chemical reduction on groundwater quality, (c) identify design and operational factors that <br /> influence the successful performance of the in-situ chemical reduction approach, and (d) generate <br /> performance, design and cost data that can be used for design of a full-scale in-situ treatment <br /> system as a possible alternative to the current groundwater extraction and treatment system. <br /> 5. A sequence of alluvial sediments underlying the MCTC facility from the water table <br /> [(approximately 60 ft below ground surface (bgs)] to depths of at least 450 bgs comprises one <br /> aquifer. This aquifer is characterized by discontinuous lenses of sand, gravelly sand, clayey silt, <br /> silty clay, and clay. The aquifer can be divided into four hydrostratigraphic subimits: a) the <br /> shallow zone (water table to 80 ft bgs),b) the 100 ft zone (approximately 80 to 120 ft bgs), c) the <br /> intermediate zone (approximately 120 feet to depths ranging from 170 to 200 bgs) and, d)the deep <br /> zone extending from below 200 ft bgs to approximately 450 ft bgs. Groundwater generally flows <br /> in a southern direction in all zones. Groundwater velocity ranges from about 0.5 to 2.3 feet per day <br /> depending on the different zones. <br />