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WORK PLANS FILE 2
Environmental Health - Public
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EHD Program Facility Records by Street Name
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DURHAM FERRY
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3500 - Local Oversight Program
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PR0544624
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WORK PLANS FILE 2
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Last modified
7/3/2019 6:03:33 PM
Creation date
7/3/2019 3:33:15 PM
Metadata
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Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
WORK PLANS
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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1 <br /> Geologica[Teclsnics/nc. Page 11 <br /> ' IRAP-Pilot Test <br /> Project No. 425.2 <br /> March 21,2005 <br /> 1 <br /> 5.0 ASSESSMENT OF REMEDIAL EFFECTIVENESS <br /> ' Pre-test soil and water quality parameter data are needed because the injection of ozone will <br /> be causing a chemical reaction in the subsurface. The chemical reaction is intended to <br /> ' destroy gasoline constituents but it can have negative affects such as increasing the solubility <br /> of metals as stated above. <br /> Water samples from all the shallow monitoring wells will be analyzed for the following <br /> constituents: <br /> • pH, EC,DO& ORP-weekly for first month, thereafter monthly <br /> • TBA,TBF, acetone (MTBE breakdown by-products)-monthly <br /> • TPH-g, BTEX and MTBE-monthly <br /> ' Hexavalent Chromium and Iron - monthly <br /> ' Above mentioned parameters will be compared with the initial concentrations on a monthly <br /> basis. After six months of operation of the system, the system will be turned off for at least <br /> 15 days before testing for the above mentioned parameters. This will provide an estimate for <br /> ' the overall effectiveness of the system in removing gasoline contamination. <br /> 5.1 Radius of Influence Determination <br /> The sparge wells are located near of monitoring wells. All the monitoring wells will be <br /> monitored to determine how long the ozone takes to affect the wells and to estimate the <br /> ' radius of influence. The concentration of dissolved oxygen (DO) in an aquifer is used as an <br /> indicator of air sparging effectiveness (source: "Analysis of Selected Enhancements for Soil <br /> Vapor Extraction", US EPA document EPA-542-R-97-007, September, 1997). This also <br /> ' applies to ozone usage as elevated DO in the wells will be an indicator that the ozone is <br /> oxidizing the subsurface with the 02 reaction byproduct present in the aquifer. <br /> ' 5.2 Plume Degradation Analysis <br /> In-situ chemical oxidation technologies generally require determining the amount of <br /> ' contaminant present and then calculating the quantity of oxidant to destroy the contaminant <br /> on a mass or weight percentage basis. The amount of TPH-g calculated to be in the ground <br /> was 6700 lbs after excavation in July 2001. In an ideal situation each molecule of ozone <br /> would react with and destroy one molecule of hydrocarbon. But other factors impede the <br /> ozone oxidation reaction including: <br /> • Micro-channeling (preferential pathways) that prevent the ozone from reaching the <br /> ' hydrocarbons that are located away from the micro-channels. <br /> • Natural organic carbon in soils that is preferentially oxidized by the ozone. <br /> • The presence of other organic and inorganic chemicals that will react with the ozone <br /> and/or oxygen. <br />
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