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WORK PLANS FILE 2
EnvironmentalHealth
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EHD Program Facility Records by Street Name
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DURHAM FERRY
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1600
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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
Fields
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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EHD - Public
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Creologkal ncwa IHC. Page 4 <br /> ' IRAP—Pilot Test <br /> Project No. 425.2 <br /> March 21,2005 <br /> ' Comparison of relative strength of oxidants <br /> ' Std. Redox Potential Relative Oxidizing <br /> Oxidant E° (Volts) Powerl <br /> Fluorine (F2) 3.0 2.23 <br /> ' <br /> Hydroxyl Radical ('OH) 2.8 2.06 <br /> -Oxygen Radical ('0) (Superoxide) 2.4 1.76 <br /> Ozone (03) 2.1 1.54 <br /> ' <br /> Hydrogen Peroxide (H2O2) 1.8 1.31 <br /> -Permanganate n04' 1.7 1.24 <br /> Chlorine Dioxide C102 1.6 1.15 <br /> ' Chlorine C12) 1.4 1.00 <br /> -Oxygen (02) 1.2 0.86 <br /> Bromine (Br2) 1.1 0.80 <br /> ' Iodine (I2) 0.8 0.54 <br /> 1 =Normalized to Chlorine,where C12= 1.0 <br /> ' Ozone sparging is an in situ treatment technology that involves pumping gaseous ozone into <br /> the saturated zone. The species generated during the ozone oxidation reaction include 03, <br /> -OH and 02. The"OH radical captures a hydrogen atom (as stated above) from a molecule of <br /> ' petroleum hydrocarbon contaminant, which then causes the contaminant molecule to become <br /> unstable and breakdown. The presence of gaseous oxygen (02) and air also causes a phase <br /> transfer (partitioning) of volatile organics from a dissolved state in water to a vapor phase. <br /> Soil geology is heterogeneous in nature; therefore, soil vapors will..11ot escape to the upper <br /> and/or lower hers of soil, and the continuous sparging of ozone will oxidize the <br /> contamination. On the other hand if the soil vapory will move towards the excavation area, <br /> ' the soil vapor extraction system will extract these vapors to treat. A second effect of ozone <br /> sparging is to enhance the biodegradation process of hydrocarbons by supplying oxygen to an <br /> otherwise anaerobic environment. By pulsing the system on and off, soil micro-channels <br /> ' repeatedly empty and then fill up with water/vapor thereby creating in-situ reactors. Ozone <br /> (with oxygen) is repeatedly introduced into the channels and this augments natural <br /> biodegradation. <br /> ' 2.2 Concerns and Limitations <br /> ' Problems associated with the use and design of an ozone sparging system include those <br /> generic to any gaseous sparging system and those relating to the chemical properties of <br /> ozone: <br /> ' Gaseous sparging system: <br /> • The movement of vapor¢ in the subsurface is influenced by the permeability of the <br /> soil. Fine grained and/or heterogeneous geology can prevent the upward migration of <br /> the vapor. <br /> • The presence of low permeability soils could cause preferential channeling of vapor <br /> ' movement thereby limitirig the radius of influence from sparge points. <br />
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