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FIELD DOCUMENTS FILE 2
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3500 - Local Oversight Program
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FIELD DOCUMENTS FILE 2
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Last modified
7/3/2019 5:58:21 PM
Creation date
7/3/2019 3:31:32 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
FIELD DOCUMENTS
FileName_PostFix
FILE 2
RECORD_ID
PR0544624
PE
3526
FACILITY_ID
FA0005206
FACILITY_NAME
GEORGES SERVICE
STREET_NUMBER
1600
Direction
W
STREET_NAME
DURHAM FERRY
STREET_TYPE
RD
City
TRACY
Zip
95376
APN
25510004
CURRENT_STATUS
02
SITE_LOCATION
1600 W DURHAM FERRY RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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EHD - Public
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George's Service <br /> Remedial Action Work Plan <br /> Project No.425.2 <br /> June 30,2011 <br /> 6. RECOMMENDED CORRECTIVE ACTION PLAN <br /> The recommended corrective action alternative is presented below. This alternative was <br /> selected based on an evaluation of the results of the 2009 SVE pilot test and our own <br /> experience with UST site remediation. In addition, GTI consulted the USEPA's "How to <br /> Evaluate Alternative Cleanup Technologies for Underground Storage Tank Sites", May, <br /> 1995. <br /> Based on the investigations conducted at the site to date, GTI recommends applying low <br /> vacuum soil vapor extraction combined with air sparging to address contamination in the soil <br /> and groundwater at the George's Service site, utilizing the two wells installed during the <br /> backfill of the soil excavation in 2002 for vapor extraction, and installing two new air sparge <br /> wells. <br /> 6.1. Air Sparging <br /> Air sparging is the process of injecting air directly into groundwater. Air sparging <br /> remediates groundwater by volatilizing contaminants and enhancing biodegradation. At <br /> higher rates of sparging, the contaminants are removed from the groundwater by physical <br /> contact with the air (i.e., stripping) and are carried up into the vadose zone (i.e., unsaturated <br /> soil). As the contaminants move into the soil, a soil vapor extraction system can be used to <br /> remove vapors. At lower sparging rates, the addition of oxygen to contaminated <br /> groundwater and soils enhances biodegradation of contaminants in and above the water table, <br /> as it acts as a nutrient for bacteria. Biodegradation is also very important result of higher <br /> rates of sparging, but mass transfer may be the dominant process until concentrations are <br /> reduced. <br /> GTI proposes to utilize air sparging to address the groundwater plume. The results of the <br /> ozone sparging pilot test from 2005 show that ozone sparging is an effective groundwater <br /> remedial alternative. However, due to the presence of hexavalent chromium in the <br /> groundwater, ozone was not a feasible remedial alternative. Air sparging will work, <br /> potentially at a slower rate which is not expected to mobilize metals. <br /> As shown in the Remedial Improvement Plans, GTI proposes three air sparging points be <br /> advanced in the former UST over-excavation backfill area to accelerate the remediation of <br /> groundwater. AS-1 is proposed to be located in the gravel backfill area, southwest of the <br /> most contaminated groundwater monitoring well MW-2. The location of AS-I was selected <br /> based on the existing location of VEW-1, with the expectation that pulsing between the <br /> sparging well and the vapor extraction well may be an effective method of remediation. AS- <br /> [ is expected to target the sand unit that extends to the north at approximately 22 feet bgs. <br /> The second air sparging well AS-2 is proposed to be located west of AS-1, in the center of <br /> the gravel backfill area. Based on the expected good hydraulic conductivity between VEW-I <br /> and VEW-2, it is anticipated that the central location of AS-2 will allow for pulsing between <br /> GeologicalTecknfesInc. 15 <br /> 4252 RAP.docx <br />
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