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SITE INFORMATION AND CORRESPONDENCE
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0508462
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
1/30/2020 12:22:14 PM
Creation date
1/30/2020 11:02:07 AM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0508462
PE
2960
FACILITY_ID
FA0008093
FACILITY_NAME
CONTINENTAL GRAIN CO
STREET_NUMBER
9504
Direction
S
STREET_NAME
HARLAN
STREET_TYPE
RD
City
FRENCH CAMP
Zip
95231
CURRENT_STATUS
01
SITE_LOCATION
9504 S HARLAN RD
P_LOCATION
99
P_DISTRICT
001
QC Status
Approved
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INFORMATION SHEETOER NO. R5-2008-0149 2 <br /> IN-SITU GROUNDWATER REMEDIATION AT SITES WITH VOLATI ORGANIC <br /> COMPOUNDS, NITROGEN COMPOUNDS, PERCHLORATE, PESTICIDES, <br /> SEMI-VOLATILE COMPOUNDS AND/OR PETROLEUM HYDROCARBONS <br /> most sites. Therefore, reductive dechlorination of VOCs requires development of <br /> anaerobic conditions within the groundwater contaminant plume. PCE can be <br /> sequentially reduced to TCE, thence to cis1,2-dichloroethylene, vinyl chloride <br /> and finally to ethane. Along the way the rate of reduction, consortium of bacteria <br /> involved in the process, and groundwater conditions may change. Reduction of <br /> VOCs may even stall at a stage if the correct conditions and bacteria are not <br /> present. Perchlorate reduction appears to occur more readily than VOCs and <br /> stalling at a particular stage in the dechlorination process does not occur <br /> In order to develop a reducing environment to achieve reduction of chlorinated <br /> hydrocarbons and perchlorate, concentrations of oxygen and nitrate need to be <br /> significantly depleted. Oxygen and nitrate are more easily reduced than the <br /> chlorinated compounds and will utilize the electrons preferentially over the <br /> chlorinated compounds. Elevated concentrations of dissolved iron and <br /> manganese may also inhibit reduction of the chlorinated hydrocarbons by being <br /> electron acceptors. <br /> There are three types of anaerobic reduction that may be occurring: <br /> • Direct Anaerobic Reductive Dechlorination is a biological reaction in <br /> which bacteria gain energy and grow as one or more chlorine atoms on <br /> the chlorinated hydrocarbon molecule are replaced with hydrogen. In this <br /> reaction, the chlorinated compound serves as the electron acceptor, and <br /> the hydrogen serves directly as the electron donor (LISEPA, 2000a). <br /> • Cometabolic Anaerobic Reductive Dechlorination is a reaction in <br /> which a chlorinated compound is reduced by a non-specific enzyme or co- <br /> factor produced during microbial metabolism of another compound (i.e., <br /> the primary substrate) in an anaerobic environment. For the cometabolic <br /> process to be sustained, sufficient primary substrate is required to support <br /> growth of the transforming microorganisms. <br /> • Abiotic Reductive Dechlorination is a chemical degradation reaction, <br /> not associated with biological activity in which a chlorinated hydrocarbon <br /> is reduced by a reactive compound. Addition of an organic substrate and <br /> creation of an anaerobic environment may create reactive compounds, <br /> such as metal sulfides, that can degrade chlorinated aromatic <br /> hydrocarbons (ITRC, 2007). <br /> Of those three, direct anaerobic reductive dechlorination is the primary process <br /> for biological reduction of VOCs. In order to accomplish the complete reduction <br /> to ethane, the appropriate species of bacteria must be present. Lacking the <br /> complete consortium of bacteria could cause the process to stall at cis-1,2-DCE <br /> and vinyl chloride. If this condition occurs, adding bacteria that are known to <br />
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