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2900 - Site Mitigation Program
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PR0540859
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Entry Properties
Last modified
1/15/2020 2:47:01 PM
Creation date
1/15/2020 2:33:19 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
WORK PLANS
RECORD_ID
PR0540859
PE
2960
FACILITY_ID
FA0023361
FACILITY_NAME
PLAY N PARK (FORMER BARNES TRUCKING)
STREET_NUMBER
1817
Direction
S
STREET_NAME
FRESNO
STREET_TYPE
AVE
City
STOCKTON
Zip
95206
CURRENT_STATUS
01
SITE_LOCATION
1817 S FRESNO AVE
P_LOCATION
01
QC Status
Approved
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INFORMATION SHEET ORDER NO. R5-2008-0149 4 <br /> IN-SITU GROUNDWATER REMEDIATION AT SITES WITH VOLATILE ORGANIC <br /> COMPOUNDS, NITROGEN COMPOUNDS , PERCHLORATE, PESTICIDES, <br /> SEMI-VOLATILE COMPOUNDS AND/OR PETROLEUM HYDROCARBONS <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 /> HRCT"", 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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