We have isolated bacterial strains capable of aerobic growth on ortho-substituted dichlorobiphenyls as sole carbon and energy sources. During growth on 2,2-dichlorobiphenyl and 2,4-dichlorobiphenyl strain SK-4 produced stoichiometric amounts of 2-chlorobenzoate and 4-chlorobenzoate, respectively. Chlorobenzoates were not produced when strain SK-3 was grown on 2,4-dichlorobiphenyl.Although bioremediation is an effective cleanup strategy for many contaminants, efforts to engineer bioremediation systems for polychlorinated biphenyl (PCB)-contaminated soils or sludges have been largely ineffective. One of the more promising PCB bioremediation strategies is sequential anaerobicaerobic treatment (1). Under anoxic conditions, highly chlorinated congeners can often be reductively dechlorinated (8,25), resulting in congeners that can potentially be degraded by aerobic bacteria. The lightly chlorinated congeners (one to five chlorines) remaining after reductive dechlorination can be either utilized as an aerobic growth substrate (12, 16) or cometabolically degraded in the presence of biphenyl (9,14).With few exceptions (5, 10), anaerobic PCB dechlorination rarely occurs at the ortho positions and generally results in accumulation of ortho-or ortho-and para-substituted congeners (19,21,27,28). Interestingly, ortho substitution of a PCB also greatly reduces aerobic biodegradability (4, 13). As reported by Furukawa (11), PCB isomers with two ortho chlorines, such as 2,2Ј-dichlorobiphenyl (2,2Ј-CB) or 2,6-CB, are rarely susceptible to aerobic cometabolic degradation. As a consequence, limited aerobic degradation of ortho-substituted congeners is a weak link in the development of effective anaerobic-aerobic PCB bioremediation strategies. Possible accumulation of ortho-substituted congeners such as 2,2Ј-CB may also have ecological and human health implications (7,22).Although numerous reports have shown that monochlorobiphenyls can serve as growth substrates (2,3,6,17,18,23), reports of unambiguous growth by natural isolates on CBs has been demonstrated only for Burkholderia sp. strain LB400 (20). To the best of our knowledge, growth on a di-ortho-substituted CB has not been demonstrated. Here we report the isolation and characterization of unique bacteria capable of using as growth substrates ortho-substituted CB congeners with chlorine substituents on both rings, including an isolate able to utilize 2,2Ј-CB.The CB-degrading bacteria were isolated from PCB-contaminated, tertiary lagoon sludge as previously described (16). One isolate (SK-3) was selected based on its ability to grow on both 4-chlorobiphenyl and 4-chlorobenzoic acid (4-CBA) (16). Another isolate (SK-4) was ultimately enriched and selected based on an ability to grow on 2,2Ј-CB.Cell growth and biotransformation of CBs were studied in Balch tubes sealed with Teflon-coated stoppers as reported previously (16). Experiments were done in a mineral salts medium (16) which was amended with 5 or 10 l of a solution of a single PCB congener dissolved in heptamethylnonane (...