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ARCHIVED REPORTS_XR0008363
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545864
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ARCHIVED REPORTS_XR0008363
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Last modified
7/21/2020 9:57:46 AM
Creation date
7/21/2020 9:40:00 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008363
RECORD_ID
PR0545864
PE
3528
FACILITY_ID
FA0004530
FACILITY_NAME
MARLOWE PROPERTY
STREET_NUMBER
4648
STREET_NAME
WATERLOO
STREET_TYPE
RD
City
STOCKTON
Zip
95215
CURRENT_STATUS
02
SITE_LOCATION
4648 WATERLOO RD
P_LOCATION
99
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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' 28 April 1995 <br /> AGE-NC-95-0103 <br /> Page 8 of I I <br />' 5 1 G ESTIMATED COST OF SOIL VAPOR EXTRACTION <br />' The costs for vapor extraction systems \aries greatly, depending upon the particular system <br /> utilized for destruction of the extracted hydrocarbon vapors (thermal destruction, carbon <br /> adsorption, etc ) However, the impacted soil at the site is somewhat laterally limited (see Figure <br />' 5) and results from the vapor test indicated extracted li}drocarbon concentrations near 3,000 <br /> ppmv Therefore, this site should not require a "large-scale" system <br />' Generally, to operate, maintain, monitor and sample S%,E systems, the cost t}prcally averages <br /> between $50,000 to $100,000 per year At many sites, the purchase of a unit is most <br /> cost-effective, most units cost bets een S35,000 and S50,000 A lease/rental of a unit generally <br />' averages between $2,500 to $5,000 per month Maintenance costs for SVE unit depend primarily <br /> on the specific unit operated <br />' 5 2 EX-SITU TREATMENT -ALTERNATIVES <br /> IAeration, bioremediation, vapor extraction, and thermal destruction can all be performed on site <br /> All four are feasible methods of remediating sandy soil contaminated ti„th gasoline The first three <br /> require the construction of a treatment cell thermal destruction does not The dirt area south of <br /> the former UST location (\\here %IW--I is located) is oN\ned b\ Properties and is <br /> currently vacant, it could be used for treatment Excq\-ited soil could be stockpiled on plastic <br /> sheeting dui 11311 the ti eatment per rod <br /> Excavated soil could also be disposed of of iec)cled at a licensed facility Off-site disposal x%ould <br /> require transport of some of the soil to a Class 11 landfill, because contamination levels exceed the <br /> limits of Class III facilities Landfills also require characterization of the contaminants, «rth one <br /> sample per 25 cubic yards and anal}sis for metals to addition to TPH and BTE&X <br /> 5 2 1 EXCAVATION <br />' The above-mentioned methods require excavation of the int (3 <br /> acted sort which is enei all the <br /> P 1 Y <br /> fastest and most e$ective method for soil remediation Ho\N ever, the impacted soil extends to <br /> depths typically not accessible to conventional excavation equipment Therefore, excavation is not <br /> practical at this site In addition, aeration limits set by the San Joaquin Valley Air Quality <br /> I Management District, sampling and analysis requirements set by landfills, and the cost of replacing- <br /> the <br /> eplacingthe disposed soil make ex-situ treatment impractical <br />
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