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ARCHIVED REPORTS XR0001669
EnvironmentalHealth
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3500 - Local Oversight Program
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PR0544513
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ARCHIVED REPORTS XR0001669
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Entry Properties
Last modified
6/14/2019 1:38:23 PM
Creation date
6/14/2019 11:04:39 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0001669
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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SJGOV\wng
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EHD - Public
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i i i ti i i <br /> 19 January 2004 <br /> i 'AGE-NC Project No 96-0235 <br /> Page 5 of 8 <br /> t <br /> } <br /> No'vem'ber 2003 <br /> TPH-g was detected in the samples collected from MW-1,MW-2 and MW-10 at concentrations of <br /> 6,200 micrograms per liter(µg/1), 10,000 µg/1 and 670 µ.g/1, respectively TPH-d was detected in'--- <br />' sample collected from MW-2 at a concentration of,12 µg/1 <br /> 3TEX compounds were detected in samples MW-1,MW-2 and MW-10 at maximum concentrations <br />' of 1,800 µg/1 benzene (MW-1), 270 µg/1 toluene (MW-2), 1,100 µg/1 ethylbenzene'(MW-2) and <br /> 1,900 µg/l xylenes (MW-2) <br /> 1 MTBE was detected in the water samples collected from MW-9, MW-10, MW-13B and MW-14B <br /> at concentrations ranging from 40µg/l(MW-13B)to 66µg/1(MW-9) Water samples analyzed from <br />' MW-2,MW-11B and MW-14B contained detectable concentrations of 1,2-DCA at 3 2 µg/1, 12 µg/1 <br /> and 27 µg/l,respectively Concentrations ofD1PE,ETBE,TAME,TBA and EDB were not detected <br /> above laboratory reporting limits in any of the water samples collected during the September 2003 <br />' monitoring event <br /> Analytical results of waterPsamples collected during the last two quarters of 2003 are summarized <br />' . on Tables 2AB and 3AB, analytical results from previous monitoring events are summarized on <br /> Tables 4 and 5 Figures 7 and 8 illustrate the September data's implication on ground water <br /> contamination plumes in upper and lower ground water intervals, respectively Figures 9 and 10 <br />' illustrate November data's implication on the ground water contamination plumes in upper and <br /> lower ground water intervals, respectively, <br /> tThe laboratory report (CTEI:Laboratory IDs 0309-076-1 through 0309-076-24), chain-of-custody i <br /> forms and the laboratory QA/QC report are included In Appendix C The laboratory report (CTELµ, <br /> Laboratory IDs 0311-090-1 through 0311-090-18), chain-of-custody forms and the laboratory , <br /> QA/QC report are included m Appendix C <br /> 1 <br /> 4.0. SUMMARY AND CONCLUSIONS ' <br /> Based on the data collected in September from the former UST cluster area, AGE finds <br /> 1 , <br /> • The shallow-screened data delineate a radial ground water flow pattern, with a net flow <br />' towards the east at a gradient of 0 004 ft/ft,the deep-screened data delineated a ground water <br /> flow direction toward the east-northeast at a gradient of 0 001 ft/ft <br /> t <br /> • TPH-g was detected in ground water samples collected from MW-9, MW-10 and EW-1 at <br />' concentrations of 220 µg/1, 1,900 µg/1 and 42,000 µg/l,respectively TPH-d was detected in <br /> wthe sample collected from EW-1 at a concentration of 16 µgill <br /> Advanced GeoEnvironmental,Inc <br /> , 4 <br /> x <br />
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