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ARCHIVED REPORTS XR0003282
EnvironmentalHealth
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2900 - Site Mitigation Program
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PR0001781
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ARCHIVED REPORTS XR0003282
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Last modified
7/3/2019 1:00:15 PM
Creation date
7/3/2019 10:38:48 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0003282
RECORD_ID
PR0001781
PE
2960
FACILITY_ID
FA0004090
FACILITY_NAME
DIAMOND WALNUT GROWERS INC
STREET_NUMBER
1050
STREET_NAME
DIAMOND
STREET_TYPE
ST
City
STOCKTON
Zip
95205
APN
155 320 19 5
CURRENT_STATUS
01
SITE_LOCATION
1050 DIAMOND ST
P_LOCATION
01
QC Status
Approved
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EHD - Public
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(:VkTc <br /> A S S O C I A T E S I N C <br /> historical parameters, which have indicated the predominant groundwater gradient direction is to <br /> the east with variation between northeast and south-southeast Figure 3 depicts groundwater <br /> elevation contours for October 19, 2004 The groundwater monitoring data are summarized in <br /> Table I Monitoring data and purge logs are provided in Attachment 1 <br /> LABORATORY ANALYSES <br /> The groundwater samples collected on October 19, 2004 were submitted to Excelchem <br /> Environmental Labs, Environmental Laboratory Accreditation Program (ELAP) #2119, in <br /> Roseville. California for analyses of hexavalent chromium (Cr +6) using EPA Method 7199, <br /> total chromium, aluminum, potassium, and sodium using EPA Method 200 7, chloride and <br /> sulfate by EPA Method 300 0, phosphorus by EPA Method 365 3, trichloroethene (TCE) and <br /> tetrachloroethene (PCE) by EPA Method 8260B, and total hardness as CaCO3 by EPA Method <br /> 234013 Groundwater samples collected from wells MW-1 through MW-9, FW and were <br /> inadvertently not analyzed for dissolved calcium Additional analyses for PCE, TCE, and <br /> Aluminum were requested by the RWQCB in an e-mail correspondence dated July 12, 2004 <br /> Cr +6 was not present above laboratory detection limits in the sample collected from the facility <br /> well Cr +6 was detected in the groundwater samples collected from monitoring wells MW-3 and <br /> MW-6 at concentrations above the California Primary Maximum Contaminant Level (MCL) for <br /> total chromium in drinking water of 0 05 milligrams per liter (mg/1) The reported Cr +6 <br /> concentration in the groundwater sample collected from MW-3 was 5 8 mg/l The reported Cr +6 <br /> concentration in the groundwater sample collected from MW-6 was 0 063 mg/l Cr +6 was also <br /> detected in water samples collected from wells MW-1, MW-2, MW-4, MW-5, MW-7, MW-8, <br /> and MW-9, but at concentrations below the MCL for total chromium The distribution of Cr +6 <br /> in groundwater is shown on Figure 4 <br /> Total chromium was detected in the groundwater samples collected from wells MW-3 and MW- <br /> 6 above the California Primary MCL for total chromium in drinking water of 0 05 mg/l The <br /> reported total chromium concentration in the groundwater sample collected from MW-3 was 4 9 <br /> mg/l The reported total chromium concentration in the groundwater sample collected from <br /> MW-6 was 0 063 mg/l Total chromium was also detected in water samples from wells MW-I <br /> MW-2 MW-4, MW-5, MW-7, MW-8, MW-9, and the facility well, but at concentrations below <br /> the MCL for total chromium <br /> Tetrachloroethene, also known as Perchloroethene (PCE) was not present above laboratory <br /> detection limits in the groundwater sample collected from wells MW-2, MW-4, MW-5 MW-6, <br /> or the facility well PCE was detected in the groundwater samples collected from monitoring <br /> well MW-9 at a concentration above the MCL for PCE in drinking water of 0 005 milligrams per <br /> liter (mg/L) The reported PCE concentration in the groundwater sample collected from MW-9 <br /> was 0 0580 mg/L PCE was also detected in water samples from wells MW-1, MW-3, MW-7, <br /> and MW-8, but at concentrations below the respective MCL for PCE The distribution of PCE in <br /> groundwater is shown on Figure 5 <br /> s lenvironmentni1625831quarterlyl4gr-2004 doe 2 <br />
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