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ARCHIVED REPORTS XR0000673
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2900 - Site Mitigation Program
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PR0522496
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ARCHIVED REPORTS XR0000673
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Last modified
2/15/2019 8:04:33 PM
Creation date
2/15/2019 3:32:13 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0000673
RECORD_ID
PR0522496
PE
2957
FACILITY_ID
FA0015317
FACILITY_NAME
FLAG CITY CHEVRON
STREET_NUMBER
6421
STREET_NAME
CAPITOL
STREET_TYPE
AVE
City
LODI
Zip
95245
APN
05532024
CURRENT_STATUS
02
SITE_LOCATION
6421 CAPITOL AVE
P_LOCATION
99
P_DISTRICT
004
QC Status
Approved
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WNg
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EHD - Public
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15 July 2002 <br />AGE -NC Project No 96-0232 <br />Page 12 of 21 <br />3 4 2 Laboratory Results of Ground Water Samples <br />During the June 2002 sampling event, TPH-g was not detected in any of the analyzed water <br />samples, however, TPH-d was detected in samples collected from MW -9B, MW -9C, MW -10A, <br />MW -10C, MW -1013, MW -11C, MW -11D MW -12 (A through D), and MW -13 (A through D) at <br />concentrations as high as 430 ,ug/l (MW -12A), TPH-mo was detected in water samples collected <br />from MW -10A and MW -12A at concentrations of 260 ,ug/l and 350 1.4g/1, respectively The <br />laboratory reports noted that the TPH-d sample chromatograms had no recognizable patterns and/or <br />a few isolated peaks Based on further laboratory review of the TPH-d sample chromatograms, the <br />laboratory further indicated to AGE that with the exception of MW -12A and MW -13A, the TPH-d <br />detections did not have typical diesel characteristics, and that the detected chromatogram peaks were <br />possibly the result of biological interference (Appendix H) <br />BTEX constituents were not detected in any of the samples collected during the June 2002 sampling <br />event However, MTBE (utilizing EPA Method 8021B) was detected in water samples collected <br />from wells MW -7, MW -8A, MW -11B, MW -11D, MW -12A, MW -13A, EW -4, EW -5, EW -8 and <br />EW -10 at concentrations as high as 200 µg/l (MW -8A) <br />MTBE (utilizing EPA Method 8260M) was detected in water samples collected from monitoring <br />wells MW -7, MW -8A, MW -9A, MW -11A, MW -11B, MW -11D, MW -12A and MW -13A at <br />concentrations as high as 250 µg/l (MW -8A), isoconcentration maps displaying the estimated extent <br />of dissolved MTBE in First Zone and Second Zone aquifer are depicted in Figures 16 and 17 MTBE <br />was detected in water samples collected from extraction wells EW -4, EW -5, EW -6, EW -8 and <br />EW -10 at concentrations as high as 29 4g/1 (EW -4), an isoconcentration map displaying the <br />estimated extent of dissolved MTBE in the area of the ground water extraction wells is depicted in <br />Figure 18 <br />1,2 -DCA and TBA were detected at well MW -13A at concentrations of 2 2 ,ug/l and 17 4g/1, <br />respectively <br />No other constituents of concern were detected above laboratory reporting limits in the water <br />samples collected during the second quarter sampling event Analytical results of ground water <br />monitoring well samples are summarized in Tables 5 and 6 The laboratory reports (McCampbell <br />Analytical Inc work order nos 0206240 and 0206271) and chain -of -custody forms are presented in <br />Appendix H <br />4.0• ADDITIONAL NPDES SAMPLING REQUIREMENTS <br />An RWQCB waste water discharge permit (NPDES permit no CAG915001) for discharge was <br />issued to Flag City Chevron by RWQCB letter dated 06 November 2000 In accordance with the <br />Advanced GeoEnvironmental, Inc <br />
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