The effects of trichloroethylene (TCE) oxidation on toluene 2-monooxygenase activity, general respiratory activity, and cell culturability were examined in the toluene-oxidizing bacterium Burkholderia cepacia G4. Nonspecific damage outpaced inactivation of toluene 2-monooxygenase in B. cepacia G4 cells. Cells that had degraded approximately 0.5 mol of TCE (mg of cells ؊1 ) lost 95% of their acetate-dependent O 2 uptake activity (a measure of general respiratory activity), yet toluene-dependent O 2 uptake activity decreased only 35%. Cell culturability also decreased upon TCE oxidation; however, the extent of loss varied greatly (up to 3 orders of magnitude) with the method of assessment. Addition of catalase or sodium pyruvate to the surfaces of agar plates increased enumeration of TCE-injured cells by as much as 100-fold, indicating that the TCE-injured cells were ultrasensitive to oxidative stress. Cell suspensions that had oxidized TCE recovered the ability to grow in liquid minimal medium containing lactate or phenol, but recovery was delayed substantially when TCE degradation approached 0.5 mol (mg of cells ), up to 90% were Tol ؊ variants, no longer capable of TCE degradation. These results indicate that a toxicity threshold for TCE oxidation exists in B. cepacia G4 and that once a cell suspension has exceeded this toxicity threshold, the likelihood of reestablishing an active, TCE-degrading biomass from the cells will decrease significantly.Trichloroethylene (TCE), a suspected human carcinogen, is one of the most widespread groundwater contaminants. Although TCE can be reductively dehalogenated under anaerobic conditions, a common end product of this reaction is vinyl chloride, which is more water soluble than TCE and is a known human carcinogen (4, 21, 48). Removal of TCE from polluted sites or industrial discharge is therefore of great concern. Although TCE has not been shown to support microbial growth under aerobic conditions, a number of bacteria are capable of degrading this compound via aerobic cometabolism. In each case examined to date, a nonspecific oxygenase catalyzes TCE transformation. Bacterial strains that use oxygenases to grow on methane, butane, propene, ethylene, ammonia, toluene, phenol, isoprene, and dichlorophenoxyacetic acid have been characterized as TCE degraders (3,8,10,11,17,18,39,45,54). Although some of these bacteria exhibit high initial rates of TCE conversion, the process is invariably nonsustainable in the absence of a growth-supporting substrate (2,19,35,49).From the biological standpoint, aerobic cometabolism of TCE by microorganisms is largely dependent on two factors: (i) cellular energy requirements and (ii) the toxicity often associated with TCE oxidation. Energy problems can be overcome by carefully controlling the concentrations of the cometabolite and growth substrate (6, 9) or by selecting or designing microorganisms that are capable of expressing the TCE-degrading oxygenase while growing on a noncompetitive substrate (29,32,41). Perhaps more problematic is the t...