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SPX CORPORATION ORDER R5-2019-0018 <br /> SPX MARLEY COOLING TECHNOLOGIES GROUNDWATER CLEANUP NPDES NO. CA0081787 <br /> final RAP amendment that concluded that the pilot study successfully demonstrated the efficacy of <br /> in-situ Cr VI reduction and authorized the full-scale implementation of the in-situ treatment at the <br /> site. The WDRs for the protection of groundwater are being implemented under separate Order <br /> R5-2007-0126 issued by the Central Valley Water Board on 13 September 2007. <br /> A. Description of Wastewater and Biosolids Treatment and Controls <br /> The treatment system at the Facility consists of an electrochemical reduction and precipitation <br /> unit (ECS) operating in parallel to an ion exchange (IX) treatment system, the overall flow <br /> process can be seen in Attachment A (Figure A-1). The IX system consists of two anion <br /> exchange vessels and a cation exchange vessel. In the anion exchange vessels, chromium <br /> (VI) in the water is adsorbed onto the ion exchange resins. In the cation exchange vessel, <br /> trivalent chromium and copper are adsorbed. The exchange process continues until the <br /> resin's exchange sites are filled and exchange capacity is exhausted. The adsorbed wood <br /> treating chemicals are stripped from the ion exchange resins and the resins are conditioned <br /> for additional water treatment in a process called regeneration. During regeneration, which <br /> would occur approximately every 2.5 days, 15,000 gallons of solution containing the stripped <br /> chemicals are removed from the IX system and processed through the electrochemical unit. <br /> A process flow diagram for the ion exchange system is shown in Attachment C (Figure C-3). <br /> As a result of in-situ remediation being conducted at the site, multiple extraction wells have <br /> met cleanup goals. Due to reduced flow rates from these idled wells, the IX system is not <br /> used any longer and is offline. <br /> The ECS unit consists of an electrochemical reduction (Andco) and precipitation process that <br /> uses iron as the reducing agent for the chromium (VI)followed by the addition of polymers to <br /> optimize settling. The effluent is then filtered prior to discharge. The solids from the clarifier <br /> are pumped and accumulated in a filter press. The filter press filtrate and mixed media filter <br /> backwash are returned to the treatment plant for further treatment. Filter press cake has <br /> been characterized as a California hazardous waste and is collected in roll off bins for off-site <br /> disposal. A process flow diagram for the electrochemical precipitation system is shown in <br /> Attachment C (Figure C-2). <br /> The site is divided into two areas, the North Yard and the South Yard. All past wood <br /> treatment activities were conducted on the North Yard. Rain falling on the North Yard is <br /> collected in a storm drain system and is passed through the treatment plant in the northeast <br /> portion of the site. Due to the past practice of storing treated wood products on the South <br /> Yard, some wood treating chemicals had been detected in the storm water runoff. The South <br /> Yard surface has been cleaned and residual contamination in pipes and ditches removed as <br /> part of the remedial actions undertaken by the Discharger. <br /> Additionally, when sufficient storm water is accumulated on the North Yard to justify <br /> treatment, the operator will manually initiate storm water treatment through the Andco system. <br /> Groundwater from selected wells will simultaneously be delivered to the ion exchange <br /> treatment system. <br /> The groundwater treatment facility is designed to treat a maximum flow up to 0.94 mgd. <br /> Groundwater is extracted from approximately 13 operative extraction wells on and off-site. <br /> The groundwater extraction system can operate in a cyclical fashion with each of the two <br /> cycles lasting 56 hours or on a continuous basis with all extraction wells pumping at rates <br /> varying from 10 to 90 gallons per minute depending on effective capture of the groundwater <br /> contamination plume. When cycling, primary groundwater extraction is alternated between <br /> the north zone and the area south of the site. Water extracted from the north zone has higher <br /> contaminant concentrations. During south zone pumping, the capacity of the treatment plant <br /> ATTACHMENT F- FACT SHEET F-5 <br />