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ARCHIVED REPORTS XR0001665
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3500 - Local Oversight Program
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PR0544513
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ARCHIVED REPORTS XR0001665
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Last modified
6/14/2019 1:02:26 PM
Creation date
6/14/2019 11:02:33 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0001665
RECORD_ID
PR0544513
PE
3528
FACILITY_ID
FA0024115
FACILITY_NAME
WEST CLAY PROPERTY
STREET_NUMBER
639
Direction
W
STREET_NAME
CLAY
STREET_TYPE
ST
City
STOCKTON
Zip
95209
APN
14707110
CURRENT_STATUS
02
SITE_LOCATION
639 W CLAY ST
P_LOCATION
01
QC Status
Approved
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> t ` <br /> JI _ <br /> I f ` <br /> 16 August 2004 <br /> AGE-NC Project No 96-0235 <br /> Page 4 of 6 t <br /> I <br /> MTBE was detected in the water samples collected from MW-9,MW-11 B,MW-12B,MW-13B and <br /> I MW-14B at concentrations ranging from 25 }Ig/1 (MW-12B) to 110 µg/1 (MW-9) Water samples k <br /> analyzed from MW-1, MW-2, MW-11B,MW-14B and EW-2 contained detectable concentrations <br /> of 1,2-DCA ranging from-2 2 µg/l (EW-2) to 29 µg/1 (MW-14B) Concentrations of D1PE, ETBE, <br /> TAME,TBA,EDB,methanol and ethanol were not detected above laboratory reporting limits in any <br /> ' of the water samples collected during the May 2004 monitoring event ; <br /> Analytical results of water samples collected during the Second Quarter of 2004 are summarized on <br /> Tables 2 and 3,analytical results from previous monitoring events are summarized in Tables 4 and 5 <br /> Figures 5 and 6 illustrate the ground water contamination plumes in upper and lower ground water <br />' intervals, respectively The laboratory report (CTEL Laboratory IDs 0405-018=1 through <br /> 0405-018-10 and 0405-030-1 through 0405-030-10),-chain of custody forms and the laboratory <br />' QA/QC report are included In Appendix C GeoTracker confirmation pages of the submitted <br /> laboratory electronic deliverable format (EDF) files are included In Appendix D <br /> 4.0. SUMMARY AND CONCLUSIONS <br /> I <br />' • Based on the data collected from the former northern UST cluster area, AGE finds <br /> • The shallow-screened data delineate a radial ground water flow pattern, with a net flow <br />' towards the northeast at a gradient of 0 003 ft/ft, the deep-screened data delineated a ground <br /> water flow direction toward the northeast at a gradient of 0 002 ft/ft Ground water gradient <br /> and flow direction observed dunng the Second Quarter 2004 were similar to'the previous <br /> 1 ' - y <br /> quarter E ' <br /> • TPH-g was detected In ground' water, samples collected from MW-9 and MW-14B 'at concentrations of 110 pg/1'and 130 µg/l, respectively <br /> ' r <br /> • MTBE was riot'detected In the,shallow-screened wells sampled during the Second Quarter <br /> 2004 MTBE was detected by EPA Method 8260B in the deep-screened wells MW-9, <br />'. MW-12B, MW-13B and MW-14B at concentrations as high as 110 µg/1 (MW-9) The <br /> " I reported MTBE concentrations were above the DHS' Pnrnary MCL of-13 pg/l in drinking j -r <br />' <br /> wafer" <br /> 1 <br /> • 1,2-DCA was detected in ground water samples,collected from, wells MW-11B and <br /> ' MW-14B,,the detected concentration exceeded the-DHS' MCL <br /> • <br /> The,most Impacted ground water appears to be centered around the former UST dispenser <br /> location The vertical extent of the contamination plume,as,well as the lateral extent east and <br /> south'of the former UST cluster, Is not well defined <br /> 1 <br /> Advanced GeoEnv►ronmental,Inc <br /> S � F <br /> I IS M1 1 <br /> I I I <br /> I I - <br />
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