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ARCHIVED REPORTS (3)
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0541087
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ARCHIVED REPORTS (3)
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Last modified
2/22/2019 8:05:11 PM
Creation date
2/22/2019 3:40:47 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
RECORD_ID
PR0541087
PE
2959
FACILITY_ID
FA0023524
FACILITY_NAME
SPX MARLEY COOLING FACILITY
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
01
QC Status
Approved
Scanner
TMorelli
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EHD - Public
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2011 Semiannual Groundwater Monitoring and Evaluation Report <br /> Full-Scale In Situ Hexavalent Chromium Reduction Treatment Implementation <br /> Former Marley Cooling Tower Site, Stockton,California January 2012 <br /> • SO4 (may be formed as calcium polysulfide (CaSX) reacts with Cr+6 or other reducible <br /> species) <br /> • General parameters (indicator of redox conditions in the treatment zone) <br /> 4.2.1 Hexavalent and Total Chromium <br /> Analytical results for total dissolved Cr and Cr+6 collected for the injection program are <br /> summarized in Table 5 and presented on Graphs 1 through 4. Cr concentration contours for the <br /> third-quarter (July 2011) monitoring and sampling event are shown in Appendix A, Figure 1 <br /> (Shallow Zone) and Figure 2 (Intermediate Zone). The fourth-quarter(October 2011) monitoring <br /> and sampling event total dissolved Cr concentrations are shown in Appendix A, Figure 3 <br /> (Shallow Zone) and Figure 4 (Intermediate Zone). <br /> 4.2.1.1 Background and Compliance Wells. Initial background sampling for the full- <br /> scale in situ Cr+6 reduction treatment implementation was completed in January 2008. During <br /> the third and fourth quarters of 2011, the Cr concentration detections in background and <br /> compliance wells ranged from 3J gg/L, J refers to the value being detected but below the <br /> reporting limit; therefore, the result in an estimated concentration, (MW-302 in July 2011 and <br /> MW-202 in October 2011) to 17 gg/L (MW-304 and MW-310 in July 2011). Cr was not <br /> detected in the background and compliance wells at concentrations above the WQO (50 gg/L) <br /> during the current reporting period. Table 6 presents the proposed upper background <br /> concentration limits for background wells in comparison to historical results and WQOs. <br /> Cr concentrations were below the proposed upper background concentration limits for the <br /> background and compliance wells. <br /> Detected concentrations of Cr+6 in the background and compliance wells in the third- and foruth- <br /> quarter 2011 sampling events ranged from 0.61 gg/L (MW-211 in October 2011) to 9.74 gg/L <br /> (MW-201 in October 2011). Cr+6 concentrations in background and compliance wells were <br /> below the WQO and the proposed upper background concentration limits for each well. <br /> 4.2.1.2 Injection Area Wells. Total dissolved Cr and Cr+6 were detected at <br /> concentrations above the WQOs in 16 of the 44 wells sampled during both the third and fourth <br /> quarters of 2011 (not including the background and compliance wells). The highest reported <br /> 0) MWH , <br /> 4-2 <br />
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