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WORK PLANS_FILE 1
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WORK PLANS_FILE 1
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Last modified
1/30/2020 3:30:38 PM
Creation date
1/30/2020 1:51:42 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
3500 - Local Oversight Program
File Section
WORK PLANS
FileName_PostFix
FILE 1
RECORD_ID
PR0545246
PE
3528
FACILITY_ID
FA0003611
FACILITY_NAME
PARKWOODS GAS & FOOD
STREET_NUMBER
1612
Direction
W
STREET_NAME
HAMMER
STREET_TYPE
LN
City
STOCKTON
Zip
95209
APN
07728002
CURRENT_STATUS
02
SITE_LOCATION
1612 W HAMMER LN
P_LOCATION
01
P_DISTRICT
002
QC Status
Approved
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EHD - Public
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�i <br /> N <br /> Engineered Approaches to In Situ Bioremediation of Chlorinated Solvents <br /> 2.4.1 Aerobic Oxidation <br /> rli <br /> hi aerobic zones of the subsurface (zones of the subsurface where oxygen is present), certain CAHs can <br /> be oxidized to carbon dioxide, water, and chloride by direct and cometabolic mechanisms (Hartman and <br /> 1 DeBont 1992; McCarty and Semprini 1994; Malachowsky and others, 1994; Gerritse and others, 1995; <br /> Bielefeld and others 1995; Hopkins and McCarty 1995). Direct mechanisms are more likely to occur <br /> with the less chlorinated CAHs (mono- and di-chlorinates). In general, the more chlorinated CAHs can <br /> be oxidized by cometabolic mechanisms, but no energy is provided to the organism. Incidental oxidation <br /> is caused by enzymes intended to carry out other metabolic functions. Generally, direct oxidation <br /> mechanisms degrade CAHs more rapidly than cometabolic mechanisms (McCarty and Semprini 1994) <br /> (refer to the following case studies in Appendix A: Aerobic Degradation in Field Demonstration at <br /> Moffett Naval Air Station, Mountain View California [Moffett Field]; Aerobic Degradation Field <br /> Demonstration at Site 19, Edwards Air Force Base, California/Edwards AFBJ; Methane Enhanced <br />;I Bioremediation Using Horizontal Wells at Savannah River Site, Aiken, South Carolina[SRS] ; and <br /> Cometabolic Bioventing at Building 719, Dover Air Force Base, Dover, Delaware[Dover Building 7191). <br /> i <br />!� Aerobic Oxidation (Direct) <br /> Aerobic oxidation (direct) is the microbial breakdown of a compound in which the compound serves as <br /> an electron donor and as a primary growth substrate for the microbe mediating the reaction. Electrons <br /> that are generated by the oxidation of the compound are transferred to an electron acceptor such as <br /> oxygen. <br /> In addition a microorganism can obtain energy for cell maintenance and growth from the oxidized <br /> i' compound (the compound acts as the reductant). In general, only the less chlorinated CAHs (CAHs with <br /> one or two chlorines) can be used directly by microorganisms as electron donors. CAHs that can be <br /> oxidized directly under aerobic conditions include DCE, DCA, VC, CA, MC, and CM (Bradley 1998 ; <br /> RTDF 1997; Harkness and others 1999). The CAHs are oxidized into carbon dioxide, water, chlorine, <br /> and electrons, in conjunction with the reduction of oxygen to water. Exhibit 2-11 shows an example of <br /> aerobic oxidation (direct) of a CAH. <br /> Exhibit 241 : Aerobic Oxidation (Direct) <br /> OXIDIZED CO + H 0 <br /> CAH + CI + energy <br /> Bacterial <br /> Enzymes <br /> OZ REDUCED H2O <br /> Source: Modified from Har mans and DeBont 1992 <br /> 2- 13 <br />
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