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FIELD DOCUMENTS AND WORK PLANS 1992-1999
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0009002
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FIELD DOCUMENTS AND WORK PLANS 1992-1999
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Last modified
2/22/2019 9:57:43 PM
Creation date
2/22/2019 2:55:03 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
FileName_PostFix
AND WORK PLANS 1992-1999
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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1. Quarterly sampling (January, April, July, and October) of all domestic supply <br /> wells, irrigation supply wells, and California Water Service Supply Wells; <br /> 2. Semi-annual sampling of select monitoring wells; <br /> 3. Annual sampling (January) of all monitoring wells, lysimeters, monitoring <br /> tubes, reclamation wells, and extraction wells. <br /> In addition to the analytical groundwater sampling, groundwater elevations are <br /> measured on a quarterly basis. Analytical results and groundwater elevation maps are <br /> reported semi-annually. <br /> PROPOSED GROUNDWATER MONITORING PROGRAM <br /> Based on review of cumulative total chromium concentration trends observed in the <br /> monitoring, extraction and reclamation wells, and the hydrogeological data including <br /> groundwater elevation maps and groundwater quality hydrographs (Dudek, January <br /> 1999), it is our opinion that reduction in the frequency of groundwater monitoring at the <br /> facility is warranted. In general, the proposed revised monitoring schedule is based on <br /> the following observations: <br /> 1. Changes in water elevations, groundwater flow directions, and the resultant <br /> dissolved chromium migration can be adequately observed on semi-annual to <br /> annual time periods. Furthermore, existing hydrogeological data adequately <br /> demonstrate capture of the dissolved chromium plume. <br /> 2. The steady decrease in dissolved chromium concentrations in many wells, the <br /> lack of detectable concentrations of dissolved chromium in many wells for <br /> several years, and reduction in the areal extent of the dissolved chromium <br /> plume, indicate that remedial activities are successfully recovering dissolved <br /> chromium. This can be seen in Figures 15 and 16, and the contaminant <br /> concentration hydrographs of wells affected by the proposed change, in the <br /> Dudek, January 1999 report. <br /> In order to reduce sampling times and costs, Dudek & Associates has put together a <br /> revised sampling schedule based on water quality hydrographs (Dudek, January 1999) <br /> that is summarized in Table 1. Those wells that have remained at low chromium <br /> concentrations for several years will be taken out of annual sampling. The goal is to <br /> reduce the number of days Geoanalytical Laboratories has to spend in the field, thus <br /> reducing costs. <br /> To optimize remedial system efficiency, and ultimately facilitate reduction in the <br /> required total pumping volume necessary for effective plume recovery and associated <br /> remedial system capacity, it is advantageous to continue to analyze dissolved chromium <br /> concentrations in groundwater samples in the reclamation wells quarterly. These data <br /> can be used to detect changes in the dissolved chromium plume without requiring <br /> frequent sampling of monitoring wells outside the plume. <br />
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