Table 1.
Category | Compounds | Aerobic degradation | Anaerobic degradation |
---|---|---|---|
Chlorinated ethenes | Tetrachloroethene (PCE) | Oxidation*1 | Reductive dechlorination116,164) |
Trichloroethene (TCE) | Oxidation115,201) | ||
Dichloroethene (DCE) cis-dichloroethene (cis-DCE) trans-dichloroethene (trans-DCE) 1,1-dichloroethene (1,1-DCE) | |||
Vinyl chloride (VC) | |||
BTEX | Benzene | Oxidation57,58,186) | *2 |
Toluene | Fumarate addition199) | ||
Ethylbenzene | Oxidation/fumarate addition16,199) | ||
Xylene o-xylene m-xylene p-xylene |
Fumarate addition96,199) | ||
Chlorinated methanes | Carbon tetrachloride (CT) | *3 | Reductive dechlorination61,146) |
Chloroform (CF) | Oxidation28) | ||
Dichloromethane (DCM) | Dechlorination (glutathione substitution)127) | Fermentation105) |
The aerobic degradation of PCE is limited, except as described by Ryoo et al. (155).
The mechanisms underlying the anaerobic degradation of benzene are unclear, although hydroxylation to phenol, methylation to toluene, and carboxylation to benzoate were proposed by Weelink et al. (199).
The aerobic degradation of CT remains ambiguous.