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2900 - Site Mitigation Program
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PR0541344
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Last modified
12/13/2019 12:30:38 PM
Creation date
12/13/2019 11:05:12 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0541344
PE
2960
FACILITY_ID
FA0023692
FACILITY_NAME
GUARDINO & CRAWFORD
STREET_NUMBER
517
Direction
W
STREET_NAME
FREMONT
STREET_TYPE
ST
City
STOCKTON
Zip
95203
APN
13721410
CURRENT_STATUS
01
SITE_LOCATION
517 W FREMONT ST
P_LOCATION
01
QC Status
Approved
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i <br /> u .. 22 November 2006 <br /> AGE-NC Project No. 95-0167 <br /> F Page 7 of 15 <br /> 5 . 1 .2 , REQUIRED SOIL CONDITIONS <br /> Operation of the blower in a vapor extraction system creates a partial vacuum in the subsurface, <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 information has been gained through the examination of soil <br /> 1 samples collected at the site. Soil in the upper 15 feet has a relatively high clay and silt content, <br /> potentially making vapor extraction less effective for this zone. Soil below 15 feet and in the <br /> saturated zone consists of sand, rendering vapor extraction as an effective remediation method. <br /> Figures 3 depicts a cross section, showing subsurface soil types at the site. <br /> 5 . 1 .3 . MONITORING ACTIVITIES <br /> _ Monitoring of vapor extraction systems involves weekly measurement ofvapor concentrations at the <br /> f inlet to the destruction unit and periodic service and repair. Systems can be equipped with an <br /> automatic telecommunication system to alert the operator of system malfunction or failure. Vapor <br /> samples should be collected monthly for laboratory analysis to monitor the efficiency of the <br /> lremediation 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 /> � J <br /> 5 . 1 .4. FEASIBILITY <br /> ' I <br /> Generally, a vacuum ofat least 0. 10 inches ofwater is required to successfully volatilize subsurface <br /> hydrocarbons. The radius of influence is often considered to be the distance from the extraction well <br /> J at which a vacuum of at least 0 . 1 inches of water is observed (EPA - A guide for Corrective Action <br /> Plan Reviewers). A vapor extraction feasibility test has not been performed at the site, however, data <br /> obtained during the installation of soil borings and monitoring wells may be useful in determining <br /> a theoretical effective radius of influence. Installation of extraction wells would be required at the <br /> site to implement an SVE system. Due to the lateral and vertical extent of contamination located <br /> beneath the main building on the property, SVE is the best way to access and remediate the entire <br /> plume, successfully. <br /> I One drawback of SVE is that not all contaminated zones of soil are remediated effectively or at the <br /> €- same rate. For instance, 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 <br /> treatment of soil lying below ground water or within the "smear" zone and ineffective treatment of <br /> longer-chain hydrocarbons (i.e., diesel, motor oil). Ground water remediation should be conducted <br /> Advanced GeoEnvironmental, Inc. <br /> Id <br />
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