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ARCHIVED REPORTS XR0000697
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0522496
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ARCHIVED REPORTS XR0000697
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Last modified
2/15/2019 7:15:49 PM
Creation date
2/15/2019 4:15:02 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0000697
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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EHD - Public
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40 31 August 2005 <br /> AGE-NC Protect No 96-0232 <br /> Page 18 of 30 <br /> utilizing the formula for an elliptic cone (V='/anabh),where `a' represents the semi-mayor axis, `b' <br /> represents the semi-minor axis and `h' represents the height of the elliptic cone For the northern <br /> segment, a semi-minor axis of 8 feet, a semi-mayor axis of 57 feet, a height of 140 feet and an <br /> average MTBE concentration of 0 077 mg/kg were used to estimate the coned elliptical volume of <br /> MTBE-impacted soil For the southern segment, a semi-minor axis of 8 feet, a semi-mayor axis of <br /> 57 feet, a height of 110 feet and an average MTBE concentration of 0 145 mg/kg were used to <br /> estimate the coned elliptical volume of MTBE-impacted soil When the data collected at the site is <br /> plotted in both plan view and cross sectional views, the apparent volume of MTBE impacted soil <br /> totals approximately 4,433 cubic yards, which yielded a total of approximately 1 54 pounds of <br /> MTBE,or an estimated 0 25 gallons of MTBE remaining in soil at the site Volume calculations are <br /> included in Appendix L <br /> 4.0. ASSESSMENT OF HYDROCARBON-IMPACTED GROUND WATER <br /> AGE has interpreted previous investigative results to indicate that a Flag City Chevron unauthorized <br /> release of MTBE occurred in the areas of the UST pit and the fuel dispensers The most intense on- <br /> site MTBE concentrations were historically detected adjacent the southwest corner of the UST area <br /> from wells MW-1 (5,700 µg/1, June 2000), EW-1 (1,800 µg/1, April 2000) and EW-2 (3,300 µg/1, <br /> July 2000) AGE previously modeled the Flag City Chevron dissolved plume to have migrated <br /> through First Zone and Second Zone ground water, approximately 180 feet westward to the area of <br /> the former Rocky's Restaurant domestic water well,at which point the plume appeared to converge <br /> with that of a Three B's Truck Plaza MTBE ground water plume Off-site towards the west, the <br /> vertical extent of the Flag City Chevron dissolved MTBE plume was modeled to have reached <br /> depths as great as 75 feet bsg (MW-1 I B) near the Rocky's Restaurant domestic water well, the <br /> maximum westward extent of the Flag City Chevron plume was most likely in the area of the former <br /> Rocky's Restaurant domestic drinking water well(RDW-1)due to the previous pumping activity of <br /> the domestic water well The estimated extent of First Zone dissolved MTBE between July 1996 and <br /> March 2005 is illustrated in Appendix H,Second Zone dissolved MTBE between March 2001 and <br /> March 2005 is illustrated in Appendix I <br /> After November 2000(pump-and-treat remediation start-up),on-site MTBE concentrations sampled <br /> from Flag City Extraction wells EW-1 through EW-10 all generally declined to either non-detect <br /> (EW-1, EW-2, EW-3, EW-6, EW-7, EW-10) or near non-detectable levels (EW-4, EW-5, EW-8, <br /> EW-9) Furthermore, on-site First Zone ground water monitoring well MW-1 had declined to non- <br /> detect MTBE levels by December 2001 and MW-4 had declined to non-detect MTBE levels by <br /> March 2001, on-site wells MW-2 and MW-5 were already at non-detectable levels prior to <br /> November 2000 On-site Second Zone well MW-8A was already at non-detect levels prior to <br /> November 2000 and well MW-9A reached non-detect levels by September 2002 <br /> Advanced GeoEnvironmental,Inc <br />
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