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Handbook of Solvents - George Wypych - ChemTech - Ventech!

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1586 Hanadi S. Rifai, Charles J. Newell, Todd H. Wiedemeier<br />

As with the ethenes, chlorinated ethanes will also undergo halorespiration.<br />

Dechlorination <strong>of</strong> 1,1,1-TCA has been described by Vogel and McCarty 38 and Cox et al., 61<br />

but understanding this pathway is complicated by the rapid hydrolysis reactions (e.g.,<br />

half-life is 0.5-2.5 yrs) that can affect TCA. 30 Finally, halorespiration has been observed<br />

with highly chlorinated benzenes such as hexachlorobenzene, pentachlorobenzene,<br />

tetrachlorobenzene, and trichlorobenzene. 62-64 As discussed by Suflita and Townsend, 64<br />

halorespiration <strong>of</strong> aromatic compounds has been observed in a variety <strong>of</strong> anaerobic habitats,<br />

including aquifer materials, marine and freshwater sediments, sewage sludges, and soil<br />

samples. However, isolation <strong>of</strong> specific microbes capable <strong>of</strong> these reactions has been difficult.<br />

23.1.3.2 Oxidation <strong>of</strong> chlorinated solvents<br />

In contrast to halorespiration, direct oxidation <strong>of</strong> some chlorinated solvents can occur biologically<br />

in groundwater systems. In this case, the chlorinated compound serves as the electron<br />

donor, and oxygen, sulfate, ferric iron or other compounds serve as the electron<br />

acceptor.<br />

23.1.3.2.1 Direct aerobic oxidation <strong>of</strong> chlorinated compounds<br />

Under direct aerobic oxidation conditions, the facilitating microorganism uses oxygen as an<br />

electron acceptor and obtains energy and organic carbon from the degradation <strong>of</strong> the chlorinated<br />

solvent. In general, the more-chlorinated aliphatic chlorinated solvents (e.g., PCE,<br />

TCE, and TCA) have not been shown to be susceptible to aerobic oxidation, while many <strong>of</strong><br />

the progeny products (e.g., vinyl chloride, 1,2-DCA, and perhaps the isomers <strong>of</strong> DCE) are<br />

degraded via direct aerobic oxidation.<br />

Hartmans et al. 65 and Hartmans and de Bont 66 show that vinyl chloride can be used as a<br />

primary substrate under aerobic conditions, with vinyl chloride being directly mineralized<br />

to carbon dioxide and water. Direct vinyl chloride oxidation has also been reported by Davis<br />

and Carpenter, 67 McCarty and Semprini, 53 and Bradley and Chapelle. 68 Aerobic oxidation is<br />

rapid relative to reductive dechlorination <strong>of</strong> dichloroethene and vinyl chloride. Although direct<br />

DCE oxidation has not been verified, a recent study has suggested that DCE isomers<br />

may be used as primary substrates. 68 Of the chlorinated ethanes, only 1,2-dichloroethane<br />

has been shown to be aerobically oxidized. Stucki et al. 69 and Janssen et al. 70 show that<br />

1,2-DCA can be used as a primary substrate under aerobic conditions. In this case, the bacteria<br />

transform 1,2-DCA to chloroethanol, which is then mineralized to carbon dioxide.<br />

McCarty and Semprini 53 describe investigations in which 1,2-dichloroethane (DCA) was<br />

shown to serve as primary substrates under aerobic conditions.<br />

Chlorobenzene and polychlorinated benzenes (up to and including tetrachlorobenzene)<br />

have been shown to biodegrade under aerobic conditions. Several studies have shown<br />

that bacteria are able to utilize chlorobenzene, 71 1,4-DCB, 71-73 1,3-DCB, 74 1,2-DCB, 75<br />

1,2,4-TCB, 76,77 and 1,2,4,5-TeCB, 77 as primary growth substrates in aerobic systems.<br />

Nishino et al. 78 note that aerobic bacteria able to grow on chlorobenzene have been detected<br />

at a variety <strong>of</strong> chlorobenzene-contaminated sites but not at uncontaminated sites. Spain 79<br />

suggests that this provides strong evidence that the bacteria are selected for their ability to<br />

derive carbon and energy from chlorobenzene degradation in situ. The pathways for all <strong>of</strong><br />

these reactions are similar, bearing resemblance to benzene degradation pathways. 79,80

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