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ARCHIVED REPORTS XR0009265
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2900 - Site Mitigation Program
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ARCHIVED REPORTS XR0009265
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Last modified
7/24/2019 1:07:16 PM
Creation date
7/24/2019 11:49:28 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0009265
RECORD_ID
PR0544690
PE
3528
FACILITY_ID
FA0005839
FACILITY_NAME
CASTLE AUTOMOTIVE REPAIR INC.
STREET_NUMBER
2315
Direction
N
STREET_NAME
EL DORADO
STREET_TYPE
ST
City
STOCKTON
Zip
95204
APN
12510017
CURRENT_STATUS
02
SITE_LOCATION
2315 N EL DORADO ST
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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Geological TeclinuS inc Page 4 <br /> Groundwater Momtormg Report <br /> Project No 723 2 <br /> December 17,2002 <br /> The detection limits for the above analyses are listed in Table 2 of Appendix A while the <br /> Y pp <br /> ' lab analytical results are presented in Appendix B <br /> As required under AB2886, the laboratory data were submitted electronically to GeoTracker <br /> on October 2, 2002 - confirmation number 8962479174 <br /> 2.0 FINDINGS AND DISCUSSION <br /> The results of the groundwater sample analysis show the following <br /> ' • The concentrations of BTEX and TPH-G continue to fluctuate in individual monitoring <br /> wells from one sampling event to the next <br /> • Intermediate well MW-101 continues to contain stable TPH-G concentrations, but <br /> benzene and toluene concentrations have fallen to non-detectable levels <br /> • Contaminant concentrations in deep well MW-201 are fluctuating from event to event <br /> Benzene and toluene concentrations have fallen to levels below the laboratory reporting <br /> limits Ethyl Benzene, Xylene and TPH-G were present at 0 4, 2 1 and 51 1 ug/l, 1 <br /> respectively MTBE was not present The contamination is probably a drilling artifact <br /> created by the use of mud rotary drilling It is noted that the contaminant concentrations <br /> in MW-201 have declined by an order of magnitude since the first monitoring event in <br /> December 2001, which supports the conclusion that the high concentrations were from a <br /> ' drilling artifact However, the continued presence of low concentration of the <br /> contaminants suggests that this inay be near the vertical extent of the plume <br /> • Figure 4 illustrates TPH-G and Benzene concentrations versus elevation in well MW-3, <br /> which lies near the core of the plume There appears to be a direct relationship between <br /> the water table and the TPH-G concentrations Benzene concentrations have stabilized <br /> in the well <br /> • Figure 5 illustrates TPH-G and Benzene concentrations versus elevation in well MW-4, <br /> which lies up gradient of the core of the plume The contaminant concentrations have <br /> ' stabilized in this well <br /> • Figure 6 illustrates TPH-G and Benzene concentrations versus elevation in deep well <br /> MW-101, which lies near the core of the plume The concentrations are approaching <br /> ' stability The steep decline in the initial concentrations suggests that the contaminants <br /> detected in the well were initially a drilling artifact Continued presences of the TPH-G <br /> compounds suggest that this well is within the plume <br /> ' • Figure 7 illustrates the TPH-G concentrations contours in the shallow wells The high <br /> concentration in well MW-2 creates a localized node Wells MW-3 & MW-5 exhibited <br /> a significant decrease in contaminant concentrations for this event The reason for this <br /> anomaly is not known, however the effect of this decrease is to displace the core of the <br /> plume to the north towards MW-2 Additional site investigation will allow a more <br /> accurate site conceptual model <br />
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