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SU0005259 SSCRPT
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SU0005259 SSCRPT
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Last modified
5/7/2020 11:31:35 AM
Creation date
9/6/2019 10:00:46 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2600 - Land Use Program
FileName_PostFix
SSCRPT
RECORD_ID
SU0005259
PE
2611
FACILITY_NAME
PA-0500469
STREET_NUMBER
5055
Direction
E
STREET_NAME
MAIN
STREET_TYPE
ST
City
STOCKTON
APN
15910007, 08, &
ENTERED_DATE
8/2/2005 12:00:00 AM
SITE_LOCATION
5055 E MAIN ST
RECEIVED_DATE
8/1/2005 12:00:00 AM
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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SJGOV\rtan
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\MIGRATIONS\M\MAIN\5055\PA-0500469\SU0005259\SSC RPT.PDF
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EHD - Public
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4.0 CHEMICAL QUALITY OF GROUNDWATER <br /> Interim performance monitoring, in the form of groundwater sample collection and laboratory analysis 1 <br /> fr <br /> for total dissolved chromium and hexavalent chromium,was performed for California Water Supply I <br /> Wells,domestic wells,and irrigation wells in January 2005. Select accessible monitoring wells were <br /> sampled for total dissolved chromium in January 2005 (Tables 3 and 4). The Annual Evaluation Report <br /> L addresses data gaps for analytical results in greater detail (Dudek, 2005). This interim sampling was I <br /> conducted in accordance with the RWQCB letter dated 14 August 1996(RWQCB, 1996). Original and <br /> field duplicate groundwater samples were analyzed by GeoAnalytical for total dissolved chromium using <br /> USEPA Method 6010,and hexavalent chromium using USEPA Method 7199 (Appendices A and B). <br /> The detection limit for total dissolved chromium was 5 ug/l. The detection limit for hexavalent I <br /> t6, chromium was 0.5 ug/l. The results are presented in Tables 3 and 4. <br /> Quality assurance/quality control(QA/QC)sampling in January 2005 included collection and analysis of <br /> field duplicate groundwater samples(Tables 3 and 4;Appendices A and B). Laboratory QAIQC <br /> documentation was included with analytical reports from GeoAnalytical (Appendices A and B). The QC <br /> report produced by GeoAnalytical included matrix spike and matrix spike duplicate samples of known <br /> ` concentration for both total dissolved chromium and hexavalent chromium, the relative percent <br /> difference between the matrix spike and matrix spike duplicate, and percent recovery of a laboratory j <br /> ` control sample(Appendices A and B). Based on the QC report supplied by GeoAnalytical, the relative <br /> percent difference between matrix spike and matrix spike duplicate samples ranged from 0.6%to 4.0% <br /> ` for total dissolved chromium, and 0.4%to 2.0% for hexavalent chromium. The percent recovery of the <br /> laboratory control samples ranged from 100.9%to 108%recovery for total dissolved chromium,and <br /> r <br /> 102%recovery for hexavalent chromium. No acceptable ranges for relative percent difference and <br /> percent recovery were provided in the laboratory analytical reports. <br /> r <br /> 4.1 Soil Flushing System <br /> r <br /> 4.1.1 January 2005 <br /> Groundwater samples were collected from 4 extraction wells, 8 lysimeters,and 9 monitoring tubes and <br /> analyzed for total dissolved chromium concentrations in January 2005. Three shallow zone extraction <br /> wells had detectable concentrations of total dissolved chromium at concentrations ranging from 8.9 ug/1 <br /> 1 - <br /> ` <br /> Marley Cooling Technologies 3909-09 <br /> Semi-Annual Groundwater Monitoring Report Dudek&Associates,Inc. <br /> October 2004/January 2005 -13- April 2005 <br />
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