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ARCHIVED REPORTS_XR0008413
Environmental Health - Public
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3500 - Local Oversight Program
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PR0545864
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ARCHIVED REPORTS_XR0008413
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Last modified
7/21/2020 10:00:58 AM
Creation date
7/21/2020 9:46:52 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
ARCHIVED REPORTS
FileName_PostFix
XR0008413
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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1 <br />' 18 February 1997 <br /> AGE-NC Project No 95-0104 <br />' Page 8 of 22 <br />' inducing air"currents" through the soil pore spaces Vapors move by convection toward the area of <br /> lowered air pressure (the extraction point) The efficiency of this process is proportional to soil <br /> porosity and permeability Qualitative insonnation has been gained through laboratory analysis of soil <br />' samples collected at the site Av -permeability at the site was approximately 6 x 10', while <br /> porosity percentage at the site was approximately 43 10 percent Generally, soil beneath the former <br /> UST area has a relatively high silty sand content in the upper thirty-feet, potentially making vapor <br />' extraction an effective remedial method for this zone Furthermore, soil between thirty and eighty- <br /> feet has a relatively high clay and silt content, potentially making vapor extraction less effective for <br /> this zone Figures 3 and 4 depict cross sections, showing subsurface soil types at the site An SVE <br /> pilot test was performed at the site, results of the pilot test are summarized in Section 3 0 <br /> One drawback of SVE is that not all contaminated zones of soil are remediated effectively or at the <br /> same rate For example, a sandy soil zone will cleanup more quickly than a silty one SVE is not <br /> usually effective in soil with high clay content Other drawbacks of SVE include ineffective treatment <br /> of soil lying below ground water or within the"smear" zone and ineffective treatment of longer-chain <br />' hydrocarbons Ground water remediation may have to be conducted concurrently with SVE to <br /> facilitate remediation of the smear zone <br /> 6 1 3 MONITORING ACTIVITIES <br /> Monitoring of vapor extraction systems involves weekly measurement of vapor concentrations at the <br /> unlet to the destruction unit and periodic service and repair Systems can be equipped with an <br /> I automatic telecommunication system to alert the operator of system malfunction or faiEuic Vapor <br /> samples should be collected monthly for laboratory analysis to monitor the efficiency of the <br /> remediation program When the concentrations of extracted vapor have decreased and stabilized after <br /> a certain period of operation, confirmation borings are drilled to collect soil samples for quantitative <br /> analysis in the laboratory to document the degree of cleanup obtained <br /> I614 FEASIBILITY <br /> Generally, a vacuum of at least 0 10 niches of water is required to successfully volatilize subsurface <br /> hydrocarbons The radius of influence is often considered to be the distance from the extraction well <br /> at which a vacuum of at least 0 1 inches of water is observed (EPA - A guide for Corrective Action <br /> IPlan Reviewers) A vapor extraction feasibility test was performed at the site in April 1995 Data <br /> obtained during the SVE test has determined a theoretical effective radius of influence at <br /> I approximately 28 feet when a transmitted vacuum of 0 1 inches of water is utihzed as a cut-off point <br /> (Figure 5 - Effective Radius of Injhience) Based upon the results of the pilot test, it appears that <br /> SVE would be an effective remediation alternative for soil at the site <br /> I <br />
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