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SITE INFORMATION AND CORRESPONDENCE
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0503634
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
5/7/2019 4:40:56 PM
Creation date
5/7/2019 4:15:53 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0503634
PE
2950
FACILITY_ID
FA0005914
FACILITY_NAME
VICTOR ROAD SHELL
STREET_NUMBER
880
STREET_NAME
VICTOR
STREET_TYPE
RD
City
LODI
Zip
95240
APN
04905032
CURRENT_STATUS
02
SITE_LOCATION
880 VICTOR RD
P_LOCATION
02
P_DISTRICT
004
QC Status
Approved
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Karen Petryna ~ `� <br /> Shell Oil Products <br /> 880 E. Victor Rd., Stockton, CA <br /> Page 3 of 5 <br /> closest point of the former UST pit and 70 feet from the most impacted <br /> monitoring well, as the delineator of the vertical extent of impacted groundwater <br /> is highly dependant on the unknown hydraulic conductivity of the unit and the <br /> flow direction — EHD believes it quite possible that this well missed the critical <br /> monitoring point. <br /> Cambria has demonstrated that a groundwater extraction rate less than 1 gallon <br /> per minute will not exert much hydrological control of the plume. If the plume is <br /> stable and not migrating as currently interpreted by Cambria, there would not be <br /> much need for hydrological control. <br /> Cambria attributes the decreasing MTBE concentration and increasing TBA <br /> concentrations to mass removal of MTBE by way of the groundwater extraction <br /> events and biodegradation of MTBE to TBA. Cambria supplied a copy of a report <br /> from a Shell study of MTBE/TBA-impacted sites that isolate biodegradation as <br /> the most likely cause of temporary rising TBA concentrations coupled with <br /> declining MTBE concentrations. EHD concurs that this is likely to be occurring on <br /> the subject site, but does not appear to be a site-wide process. It appears that <br /> the bioconversion of MTBE to TBA occurs primarily in the immediate vicinity of <br /> the well borings. <br /> The analytical data from samples collected from MW-4 during the batch <br /> extraction events demonstrate an abrupt decline of TBA and increase of MTBE <br /> concentrations. Plots of the data show that at the conclusion of each 5-day <br /> extraction event the TBA concentrations are not even close to stabilizing and <br /> MTBE concentrations are at least 30,000 ppb. This indicates to EHD that the well <br /> bores are probably influencing the surrounding groundwater chemistry and <br /> biologic response. <br /> Assuming that there is minimal drawdown during the less than 1-gallon-per- <br /> minute extraction, that the saturated section against the MW-4 screen is 10 feet <br /> thick, and that the soil has a 20% effective porosity, EHD estimates that with a <br /> 5,000-gallon extraction event, the last water into the well traveled approximately <br /> 10 feet. It would appear that the normal 3 to 4 well volumes commonly utilized for <br /> purging is not adequate at this site to get samples representative of the <br /> predominant aquifer conditions. <br /> Cambria concludes that GWE was effective and EHD believes that it is still <br /> effective for mass removal. This is based on a recovered mass of 8 pounds <br /> MTBE in nearly 20,000 gallons of water extracted. EHD does not concur with <br /> Cambria's conclusion that no known sensitive receptors are threatened and <br /> thereby there is no necessity for engineered mass removal or hydraulic control. <br /> Intuitively, any migration of impacted groundwater potentially impacts additional <br />
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