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ARCHIVED REPORTS XR0001921
Environmental Health - Public
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3500 - Local Oversight Program
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PR0544497
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ARCHIVED REPORTS XR0001921
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Last modified
5/28/2019 3:57:23 PM
Creation date
5/28/2019 3:08:38 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0001921
RECORD_ID
PR0544497
PE
3528
FACILITY_ID
FA0003687
FACILITY_NAME
OLD TRUCK STOP, THE
STREET_NUMBER
3535
STREET_NAME
CHEROKEE
STREET_TYPE
RD
City
STOCKTON
Zip
95205
APN
13206009
CURRENT_STATUS
02
SITE_LOCATION
3535 CHEROKEE RD
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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r <br /> , t <br /> r , <br />' 16 August 2001 ry <br /> AGE-NC Project No 97-0312 <br />' Page 14 of 20 <br />' 8 1 1 Treatment Methods <br /> The documented concentrations of' dissolved,hydrocarbons on the site are,not likely to trigger a requirement for treatment of the extracted water The Maximum Containment Levels (MCLS) for <br /> benzene(1 0 µg/l) and taste and odor threshold for TPH-g(5 µg11) and TPH-d (100µg/1) are locally <br /> exceeded in the areaofUST-1 and UST-5, but do not appear to have a significant vertical or areal <br />' extent Two ofthe most common methods ofwater treatment are air stripping and carbon adsorption <br /> Air stripping involves removal of volatile organic compounds from ground water by promoting the <br /> transfer o�contaminants from the dissolved phase to the vapor phase Carbon adsorption utilizes <br /> i granular activated carbon to simply"filter" organic compounds out of ground water <br /> ' t , <br /> A third, but less common method of above-ground treatment of water is bioremediation t <br /> iContaminated ground water is "treated" by adding hydrocarbon-degrading microbes or by <br /> augmenting natural hydrocarbon degradation activities with the introduction of nutrients <br /> i <br /> 812 Feasibility <br /> iAquifer testing has not been performed at the site However, based on analysis of soil samples <br /> collected during previous investigations,certain site-specific assumptions can be made regarding the <br /> i feasibility of ground water extraction at the site The subsurface profile of the site is relatively <br /> homogenous, consisting predominantly of fine-grained soil types such as silt, clayey silt, sandy silt <br /> and uldy T'y-lIedlly, boils of this IIaLiIIC rite not U 1n,,A t,-re i to bu higlhly_«.dlu i,vc� to Srounu VV aci <br /> I extraction Based on pumping tests at sites with similar soil types, pumping rates of approximately <br /> I- to 2-gallons per minute would be expected However, heavier chain hydrocarbons, like those <br /> found at the site,tend to be somewhat immpbile in water, adsorbing to fine-grain soil particles, and <br /> Imay require an extended pumping period to approach regulatory clean-up goals <br /> The poor cost/benefit potential for a"pump and treat" system at the site should also be considered <br /> The relatively expensive start-up costs associated with the system do not appear to be fiscally <br /> appropriate for a short period of effective remediation, especially if clean-up goals may not be met <br /> Based on the soil type,contaminant characteristics and low cost/benefit potential,a"pump and treat' <br /> remediation system is believed to have a limited feasibility <br /> 813 Duration , <br /> IBased on an extraction rate of approximately 1 to 2 gallons per minute, the majority of extractable <br /> hydrocarbon-impacted ground would be extracted within a I- to 2-year period <br /> Advanced GeoEnvlronmental,Inc <br /> i <br />
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