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FIELD DOCUMENTS AND WORK PLANS 2004-2014
Environmental Health - Public
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FIELD DOCUMENTS AND WORK PLANS 2004-2014
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Last modified
2/22/2019 7:04:53 PM
Creation date
2/22/2019 3:01:40 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
FileName_PostFix
AND WORK PLANS 2004-2014
RECORD_ID
PR0009002
PE
2960
FACILITY_ID
FA0004040
FACILITY_NAME
SPX COOLING TECHNOLOGIES INC
STREET_NUMBER
200
Direction
N
STREET_NAME
WAGNER
STREET_TYPE
AVE
City
STOCKTON
Zip
95215
APN
14331007
CURRENT_STATUS
01
SITE_LOCATION
200 N WAGNER AVE
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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State of California—California Environmental Protection Agency Department of Toxic Substances Control <br /> NEGATIVE DECLARATION <br /> Department of Toxic Substances Control <br /> Site Mitigation&Brownfields Reuse Program <br /> 8800 Cat Center Drive <br /> Sacramento, CA 95827 <br /> Subject: Z DRAFT❑ FINAL ❑ MITIGATED <br /> Project Title:Former Marley Cooling Tower Corporation Facility <br /> State Clearinghouse No.: <br /> Project Location: SPK, formerly MCTC is located at 200 North Wagner in Stockton; Califomia 95205 in the County of San <br /> Joaquin. Former operations were performed on two adjacent properties (referred to as North & South Yard) that are <br /> bisected by the Stockton Terminal & Eastern rail line. The facility Is bounded on the north and east by light industry and <br /> the Stockton Diverting Canal, on the west by Franklin High School's athletic field, and on the south and southeast by <br /> residential areas. <br /> Project Description: The Department of Toxic Substances Control is proposing to approve a Remedial Action Plan <br /> Amendment (RAP Amendment) pursuant to the authority granted under Chapter 6.8, Division 20, California Health & <br /> Safety Code (H&SC) at the Marley Cooling Tower Company (MCTC)Site, The objective of this remedial action is 1) to <br /> modify the current groundwater remedy to implement in-situ chromium reduction through injection of calcium polysulfide <br /> and ethanol (reductant solution); and 2) install horizontal welts and re-initiate flushing of deep soils to flush chromium to <br /> groundwater, where [t will encounter the reductant solution. if groundwater data suggests favorable site-wide results, <br /> phase out groundwater extraction, treatment,and discharge to the Stockton Diverting Canal. <br /> Remediation of subsurface soils beneath the retort pit area and the underlying groundwater has not been completed and <br /> is the subject of this RAP Amendment. While the dissolved chromium plume has reduced from the maximum extent <br /> (August 1989) in the shallow and intermediate zone with the operation of the groundwater pump and treat system, <br /> remediation time is uncertain. A solution containing potable water, calcium polysulfide that Is approved by State of <br /> Callfomia water agencies for well head rehabilitation activities and groundwater treatment of metals-impacted sites, and <br /> ethanol will be injected into groundwater to physically change the hexavalent chromium contamination in groundwater to <br /> the trivalent form, which is less toxic and not mobile in the subsurface environment. The approach proposed in the RAP <br /> Amendment has been successfully pilot-tested at the Site and is expected to clean up the groundwater in approximately <br /> three years as opposed to the current 17-year estimated cleanup time for the existing pump and treatment system. The <br /> injection solution application pilot-tested at the Site has been used at other multiple sites and has not displayed adverse <br /> effects on the long-term groundwater quality, Project activities include the following: <br /> 1. Enhance the existing soil flushing system which operated underneath the former retort pit area between 1992 <br /> and 2003. This enhanced system will be accomplished by the installation of an estimated 5 horizontal wells <br /> approximately 15 to 20 feet below the top of the retort pit cap, which is below the zone of the most significant <br /> arsenic-impacted sail. Two wells will be located in the area of the former retort pit with well screen lengths <br /> extending approximately 160 feet. Three wells will be located east of the former retort pit, in an area formerly <br /> used for solution storage in aboveground storage tanks. The screen length of the three wells will be <br /> approximately 85 feet. Drilling angles and horizontal directional drilling technology will be employed. This will <br /> enable better distribution of flushing water without disturbing the existing retort pit cap or the near surface <br /> arsenic/copper contamination underneath. <br /> 2. Flush all wells with reductant solution to mobilize and treat the chromium from the vadose zone to <br /> groundwater. The effluent water from the treatment plant will be piped to a holding tank for use as the reductant <br /> solution. From the holding tank the effluent water will be piped in parallel by manifold directly to the horizontal <br /> wells at specified rates. The two deep horizontal wells will deliver the reductant solution in the low part of the <br /> vadose zone and groundwater beneath the retort pit area. An initial dosing of reductant solution will be utilized <br /> in the two deep wells and will be determined when specific volumes and concentrations are fully evaluated. If <br /> necessary, periodic redosing would be performed. <br /> 3. Routine operations and monitoring inspections will be performed weekly to ensure that the system is <br /> functioning correctly. Personnel will inspect all aboveground piping, fittings, and all other associated equipment <br /> and make repairs as needed. <br /> DTSC 1327(110&06) <br />
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