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2900 - Site Mitigation Program
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PR0505548
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
5/17/2019 9:18:25 AM
Creation date
5/17/2019 8:58:06 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0505548
PE
2960
FACILITY_ID
FA0006852
FACILITY_NAME
OCCIDENTAL CHEMICAL CORP
STREET_NUMBER
1904
Direction
W
STREET_NAME
CHARTER
STREET_TYPE
WAY
City
STOCKTON
Zip
95205
APN
16302041
CURRENT_STATUS
01
SITE_LOCATION
1904 W CHARTER WAY
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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EHD - Public
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INFORMATION SHEET ORDER NO. R5-2008-0149 4 <br /> IN-SITU GROUNDWATER REMEDIATION AT SITES WITH VOLATILE ORGANIC <br /> COMPOUNDS, <br /> SEEMI-VOLATILE COMPOUNDS A Dl/ PERCHLORATE, <br /> OR PETROLE MPESTICIDES, <br /> periodically. The soluble substrates are consumed rather quickly and must be <br /> frequently replenished. <br /> Substrates that are viscous are less mobile than soluble substrates, but they tend <br /> to last longer in the subsurface. Slow release materials such as vegetable oil or <br /> HRCTM, which are intended to be long lasting, may require a single or limited <br /> number of injections. The low mobility of viscous substrates may lead to non- <br /> uniform distribution and require different application mechanisms to achieve the <br /> desired distributions. These substrates are relatively immobile and rely on <br /> advective and dispersive qualities of soluble compounds (lactic acid for the HRC <br /> and metabolic acids for the oil) to deliver them throughout the subsurface (ITRC, <br /> 2007). <br /> Moderate viscosity fluids such as emulsions of vegetable oil have a relatively <br /> high mobility as compared to solid or highly viscous materials that allows more <br /> uniform distribution within the aquifer. Emulsified oils slowly release hydrogen <br /> through fermentation of fatty acids. Other moderate viscosity substrates that <br /> could be used include, chitin, whey and oleate. <br /> Oxidative Environment Processes <br /> As with reductive processes, oxidation processes can be either chemically or <br /> biologically induced. A chemical oxidant removes electrons from constituents in <br /> the vicinity of the oxidant and the oxidant becomes reduced. In a biological <br /> oxidation process, one compound is the electron donor and another compound is <br /> the electron acceptor. An example of biological oxidation happens with fuel <br /> contaminants in groundwater. In an aerobic environment, fuel can provide the <br /> carbon and the electrons for microbial metabolism, and the oxidizing agent is <br /> oxygen, which is the electron acceptor. In the absence of oxygen, nitrate also <br /> serves as an electron acceptor. The fuel becomes degraded as it is oxidized. <br /> Remediation of groundwater pollution, including VOCs, benzene, toluene, <br /> ethylbenzene, xylenes, organic pesticides, munitions (i.e., HMX, RDX), <br /> petroleum hydrocarbons or MTBE can potentially be achieved using chemical or <br /> biological oxidation processes. This involves injecting oxidants directly into the <br /> source and the downgradient plume, or delivering oxidants by means of a <br /> groundwater recirculation system. The oxidant reacts with the pollutants, <br /> producing innocuous substances such as carbon dioxide, water, and chloride. <br /> The four main chemical oxidants used are permanganate, peroxide, persulfate <br /> and ozone. <br /> The ability of the oxidant to react with a certain contaminant in the field depends <br /> on kinetics, stoichiometry, thermodynamics and delivery of the oxidant. On a <br /> microscale, kinetics or reaction rates are the most important. The rates of <br />
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