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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
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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 /> 4.3 FIELD PARAMETERS <br /> Field parameters were measured at each well before sample collection, and results are <br /> summarized in Table 4. The pH, temperature, EC, ORP, and DO measurements are discussed <br /> below. Field sampling logs are provided in Appendix B. Field parameter measurements for pH, <br /> EC, and ORP are also presented on Graphs 1 through 53. <br /> Field measurements during the third and fourth quarters of 2011 showed the pH in the wells was <br /> generally within the range of 6.5 to 8 standard units. Results from the current period were <br /> generally consistent with trends since the baseline sampling event in 2008. Injection of the <br /> alkaline CaSX solution can cause a rise in pH in influenced wells. This effect has been observed <br /> in multiple wells at the Site, but tends to decrease over time due to the buffering capacity of the <br /> native soil and groundwater(for example, see Graphs 43, 52, and 53). <br /> Groundwater sample temperatures were generally within the range of 19 to 23 degrees Celsius, <br /> and generally consistent with data collected since the baseline sampling event. Temperature <br /> readings can be variable due to air temperature and the time that elapses before the reading is <br /> collected. <br /> EC is a direct measure of the TDS concentration of a water sample; hence, the behavior is <br /> consistent with the observed changes in TDS. In general, EC measurements closely match the <br /> trends described for TDS in the preceding section. The most dramatic changes in EC <br /> measurements during quarterly sampling events appear to correlate with periods of treatment <br /> solution injection. <br /> ORP is a measure of the general oxidizing or reducing conditions in the saturated zone. <br /> Generation of a strongly reducing environment enhances the reduction of Cr+6 to the trivalent <br /> state. Negative ORP readings represent reducing conditions, which are generally conducive to <br /> removing Cr from groundwater. Of the field parameters measured, ORP is generally the most <br /> indicative of remediation potential. However, site data show that a negative ORP is not <br /> necessary for Cr+6 reduction to occur (see Graphs 17, 23, 24, 49, and 51). Baseline sampling <br /> indicated that the saturated zone was at a positive ORP, ranging from 31 to 480 millivolts (mV) <br /> in the groundwater of the Shallow and Intermediate zones. This is typical of groundwater that <br /> (a mWH <br /> 4-9 <br />
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