Physiological Characterization of a Bacterial Consortium Reductively Dechlorinating 1,2,3- and 1,2,4-Trichlorobenzene

A bacterial mixed culture reductively dechlorinating trichlorobenzenes was established in a defined, synthetic mineral medium without any complex additions and with pyruvate as the carbon and energy source. The culture was maintained over 39 consecutive transfers of small inocula into fresh media, enriching the dechlorinating activity. In situ probing with fluorescence-labeled rRNA-targeted oligonucleotide probes revealed that two major subpopulations within the microbial consortium were phylogenetically affiliated with a sublineage within the Desulfovibrionaceae and the gamma subclass of Proteobacteria. The bacterial consortium grew by fermentation of pyruvate, forming acetate, propionate, CO₂, formate, and hydrogen. Acetate and propionate supported neither the reduction of trichlorobenzenes nor the reduction of sulfate when sulfate was present. Hydrogen and formate were used for sulfate reduction to sulfide. Sulfate strongly inhibited the reductive dechlorination of trichlorobenzenes. However, when sulfate was depleted in the medium due to sulfate reduction, dechlorination of trichlorobenzenes started. Similar results were obtained when sulfite was present in the cultures. Molybdate at a concentration of 1 mM strongly inhibited the dechlorination of trichlorobenzenes. Cultures supplied with molybdate plus sulfate did not reduce sulfate, but dechlorination of trichlorobenzenes occurred. Supplementation of electron-depleted cultures with various electron sources demonstrated that formate was used as a direct electron donor for reductive dechlorination, whereas hydrogen was not.Chlorobenzenes are widespread pollutants and accumulate in the food chain due to their hydrophobicity and strong persistence against chemical and microbial degradation (34). Anaerobic reductive dechlorination of chlorinated benzenes was demonstrated for enrichment cultures from biofilm reactors, sewage sludge, river sediment, and soil (3, 4, 15, 16, 22, 31, 37). Dechlorination pathways for all multiply chlorinated benzenes were elucidated (4, 15). Some dechlorination patterns can be rationalized by thermodynamic considerations (3, 13), but little is known about the microorganisms participating in chlorobenzene dechlorination.Anaerobic bacteria transforming chlorobenzoates and/or chlorophenols have been isolated in pure cultures (5, 7, 18, 27, 39, 40, 45, 48). Desulfomonile tiedjei (12), strain 2CP-1 (7), Desulfitobacterium chlororespirans (39), and Desulfitobacterium sp. strain PCE1 (18) grow anaerobically by chlororespiration. So far, it has not been possible to evaluate whether the anaerobic dechlorination of chlorobenzenes proceeds via a similar mechanism, since pure cultures are not available.While the effect of oxygen and nitrate on the dechlorination of chloroaromatics is reported to be negative for most cultures (32), the effect of sulfur oxyanions is controversial. Some reports stated an inhibitory role of sulfate in the reductive dehalogenation of various chlorinated or fluorinated aromatics (17, 19, 25, 26); other studies found only slight inhibition (24), no inhibition (14), or even a stimulated rate of dechlorination (17, 23). For one mixed culture, the mineralization of chlorophenols was concomitantly coupled to the reduction of sulfur oxyanions (20, 21). With pure cultures of D. tiedjei, it could be shown that sulfite and thiosulfate inhibited the dechlorination of 3-chlorobenzoate in growing cells, nongrowing cells, and cell extracts, while sulfate inhibited dechlorination only in growing cells (46).The high toxicity (22) and the low solubility of chlorobenzenes in water prevented the successful isolation of bacteria with chlorobenzenes as electron acceptors. It is therefore essential to study alternative electron acceptors that could be used by chlorobenzene-dechlorinating bacteria and that could substitute for chlorobenzenes during enrichment and isolation. Information about reductive dechlorination of chlorobenzenes in the presence of other electron acceptors is also needed for the evaluation of dechlorination processes at natural sites and for in situ remediation projects. To our knowledge, detailed studies of the effects of alternative electron acceptors on the dechlorination of chlorobenzenes have not been reported so far.The aim of the present study was to describe the physiological properties of a mixed culture effectively dechlorinating trichlorobenzenes and to determine the effects of various specific inhibitors and alternative electron acceptors. For these experiments, we used a stable, sediment-free mixed consortium growing in a defined, synthetic mineral medium. This consortium has been established in our laboratory from a fluidized bed bioreactor (1, 33) and reductively dechlorinates 1,2,3-trichlorobenzene to 1,3-dichlorobenzene and 1,2,4-trichlorobenzene to 1,4- and 1,3-dichlorobenzene. By inhibiting the activity of methanogenic bacteria using the specific inhibitor bromoethanesulfonate (BES), we showed that dechlorination occurs independently from methanogenic bacteria (1), as has also been shown for other enrichment cultures dechlorinating chlorobenzenes (22, 31).