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PR0526394
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Last modified
5/27/2021 11:39:23 AM
Creation date
5/27/2021 10:35:45 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
FIELD DOCUMENTS
RECORD_ID
PR0526394
PE
2960
FACILITY_ID
FA0017859
FACILITY_NAME
STOCKTON REDEVELOPMENT AGENCY
STREET_NUMBER
56
Direction
S
STREET_NAME
LINCOLN
STREET_TYPE
ST
City
STOCKTON
Zip
95203
APN
13737003
CURRENT_STATUS
01
SITE_LOCATION
56 S LINCOLN ST
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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L & M OPERABLE UNIT- FIRST QUARTER 2012 SITE STATUS, REMEDIAL SUMMARY, <br />AND GROUNDWATER MONITORING REPORT <br />Groundwater Monitoring and Sampling <br />April 30, 2012 <br />I:\Tidewater\TW Stockton (P2A)\QMRs\2012\1Q12\1Q12 QSSR QRSR QMR Stockton_FINAL.doc 2.12 <br />the stated QC limits for percent recovery, due to the analyte concentrations already present in <br />the un-spiked sample. This may indicate a possible bias for the reporting accuracy. The LCS <br />percent recovery was within QC limits indicating accuracy in reporting. RPD values were within <br />QC range in the MSD indicating precision in reporting. The reported values are considered <br />valid. <br />The MS associated with sample MW-16 for the analyte tertiary butyl alcohol was outside of the <br />stated QC limits for percent recovery, due to the analyte concentrations already present in the <br />un-spiked sample. This may indicate a possible bias for the reporting accuracy. The LCS <br />percent recovery was within QC limits indicating accuracy in reporting. RPD values were within <br />QC range in the MSD indicating precision in reporting. The reported values are considered <br />valid. <br />The surrogate 2,4,6-tribromophenol was out of QC limits for sample MW-24 due to matrix <br />interference. This may indicate a possible bias for the analysis. The method blank surrogate <br />spike was within QC limits; therefore, the sample outlier is not anticipated to affect the reported <br />values. <br />It should be noted that the MRL for chloromethane was raised in samples MW-42 and MW-59 <br />and the MRL for chloroethane was raised in sample MW-59 due to the presence of an <br />interfering compound. <br />Validation issues with report number 80125: <br />The RPD values associated with sample MW-51 for the analyte dissolved chromium was <br />outside of the stated QC limits by approximately 0.3 percent. This may indicate a possible bias <br />for the reporting precision. The LCS and LCSD percent recoveries were within QC limits <br />indicating accuracy in reporting. Since there is no RPD value to confirm precision in reporting, <br />the reported dissolved chromium may be biased; however, dissolved chromium values are <br />within historical limits. <br />2.5 FIRST QUARTER 2012 C-ZONE GROUNDWATER RESULTS <br />2.5.1 C-Zone Groundwater Gradient Data <br />C-Zone groundwater elevations at the Site ranged from 5.83 ft below MSL in well MW-64 to <br />5.44 ft below MSL in well MW-65 (Table 3 and Figure 17). Groundwater gradient during 1Q12 <br />in the C-Zone was calculated for three sections of the Site (central, north, and east). In the <br />central portion of the Site, groundwater flow direction was to the west with an approximate <br />hydraulic gradient of 0.001 ft/ft. In the northern part of the Site, groundwater flow direction was <br />to the south-southeast with an approximate hydraulic gradient of 0.0009 ft/ft. In the eastern part <br />of the Site, groundwater flow direction was to the northeast with an approximate hydraulic <br />gradient of 0.001 ft/ft (Figure 17). Historical groundwater flow direction and gradient data are <br />summarized in Table 8, and vertical gradients summarized in Table 9. The C-Zone <br />groundwater elevation contour map for the January 17, 2012 monitoring event is included as <br />Figure 17.
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