Dehalobacter
A Microbial Biorealm page on the genus Dehalobacter
Classification
Higher order taxa:
Bacteria; Firmicutes; Clostridia; Clostridiales; Peptococcaceae; Dehalobacter
Species:
Dehalobacter restrictus PER K23, Dehalobacter sp. E1, Dehalobacter sp. TCA1, Dehalobacter sp. MS Dehalobacter sp. WL
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NCBI: Taxonomy Genome |
Description and Significance
Dehalobacter restrictus is a rod shaped gram-negative obligate anaerobe found in deep soil sediments and groundwater aquifers and is phylogenetically related to several halorespiring genera like Desulfitobacterium and Desulfosporlosinus. It is a typical representative of Dehalobacter spp., which are capable of reductive dechlorination of chlorinated ethenes and chlorinated ethanes (1, 2) and fermentative dehalogenation of Dichloromethane (DCM) (3). These metabolic pathways make them relevant to bioremediation of ground water aquifers contaminated with chlorinated solvents (4). To date, several strains of Dehalobacter have been isolated (1, 3, 5-7)."
Genome Structure
The whole genome of Dehalobacter restrictus PER- K23 was recently sequenced revealing critical insights into phylogeny and metabolic capabilities of the genus. The 2,943 kbp long genome contains 2,826 protein coding and 82 RNA genes, including 5 16S rRNA genes. Interestingly, the genome contains 25 predicted rdase genes, the majority of which appear to be full length. The rdase genes are mainly located in two clusters, suggesting a much larger potential for organohalide respiration than previously anticipated (11).
Cell Structure
Dehalobacter restrictus cells are rod shaped, 2-3 µm in length and 0.3-0.5 µm in diameter with tapering ends. There is a single lateral flagellum at one end indicating that the cells are motile. The cells do not form spores under substrate and temperature induced stress. Cell wall stains gram negative and is composed of peptidoglycan type A3ϒ enveloped by a layer of proteinaceous surface layer (S – layer) (5)
Ecology and Pathogenicity
Dehalobacter spp. are found in anaerobic environments like deep soils, groundwater aquifers, and river sediments. They compete with methanogens and iron reducers found in their habitat for hydrogen and other vital nutrients. All known Dehalobacter strains are non pathogenic.
Growth, Isolation and Cultivation
Dehalobacter restrictus is obligate anaerobic chemolithoheterotrophs that use chlorinated aliphatic and aromatic compounds as electron acceptors via reductive dehalogenation and hydrogen as the sole electron donor. Acetate serves as a carbon source. It was first isolated from an anaerobic fluidized bed reactor dechlorinating PCE (5). In a lab setting, Dehalobacter restrictus is either grown in anaerobic batch microcosms or a chemostat using a highly reduced medium. Generally, isolates are fed with pure dihydrogen as electron donor and a chlorinated compound of interest (8). (e.g. Tetrachloroethylene (PCE), 1,1,2 Trichloroethylene (TCE), Chloroform (CF), 1,1,1 Trichloroethane (1,1,1 TCA), DCM). Because of their restricive nutrional needs, isolates are hard to maintain and grow. As a result, Dehalobacter restrictus is often grown as mixed cultures consisting of acidogens and methanogens in order to supplement nutritional requirements (8). Another advantage of maintaining Dehalobacter in such a consortium is that electron donors other than hydrogen (e.g. Ethanol, lactate) can be fermented to yeild hydrogen as well as acetate which is then used up by Dehalobacter restrictus (8). Nevertheless, the choice of electron donors and accpetors are based on specific strains. Growth is sensitive to temperature and pH. The optimum ranges are 25.0 - 35.0 ºC and 6.8 to 7.6). pH is regulated using 0.1 M KOH or NaOH (8).
Metabolism
Dehalobacter restrictus has unique metabolic pathways that make them vital for bioremediation of several key recalcitrant environmental contaminants (4).
Reductive dehalogenation
Reductive dehalogenation is the reduction of halogenated aliphatic and aromatic compounds using hydrogen as an electron donor. Microbially mediated reductive dehalogenation linked to growth is referred to as organohalide respiration. In addition to Dehalobacter restrictus, numerous microbial genera mediate organohalide respiration (e.g. Dehalococcoides, Dehalogimonas, etc.). When a chlorinated molecule is used as electron acceptor for organohalide respiration, and it is thus termed as microbially mediated reductive dechlorination. In this process, the chlorine atom on a chlorinated molecule is replaced by a hydrogen atom using a reductive dehalogenase enzyme (rdase) like pceA.
Dehalobacter restrictus accepts chlorinated solvents, PCE and TCE, as electron acceptors. However, reductive dechlorination is incomplete and stops at cis-1,2 dichlorethene (cDCE). Dehalobacter Strain Known electron acceptors End Products Source PER K23 PCE, TCE cDCE (5) TCA1 1,1,1 TCA, 1,2 DCA Chloroethane (9) MS CF, 1,1,1 TCA, 1,2DCA DCM (10)
Mixed populations of Dehalobacter spp. have also been shown to mediate reductive dehalogenation of 1,2 dichlorobenzene, monochlorobenzene, polychlorinated biphenyl and other recalcitrant chlorinated compounds.
Fermentation of Dichloromethane
Several different strains of Dehalobacter spp. have been known to degrade CF, and 1,1,1 TCA resulting in DCM or chloroethane, these end products often persisted and did not undergo further reductive dechlorination. However, a novel enrichment culture derived from pristine river sediment revealed another key dehalogenation pathway associated with Dehalobacter spp. This enrichment culture degraded DCM using fermentative dehalogenation. The resulting end products were acetate, methane, and chloride, which are environmentally benign.
Significance
PCE and TCE are the predominant contaminants at hazardous waste sites in the United States (12). Although less prevalent, dichloromethane (DCM) is also found at a number of sites. Occasionally, the two types of contaminants are found comingled. PCE, TCE and DCM are excellent organic solvents and were used widely in dry cleaning, paint stripping and degreasing after 1960 (13). As of January 2000, the Environmental Protection Agency (EPA) classified PCE and DCM as likely to be human carcinogens by all routes of exposure while TCE is classified as a carcinogenic to humans by all routes of exposure (13). Studies indicate that chronic exposure to DCM can increase the probability of getting liver and lung cancer and benign growths in humans. The maximum contaminant level goal (MCLG) and the maximum contaminant level (MCL) for all three contaminants have been set to 0 and 0.005 mg/L, respectively (14). Bioremediation has emerged as a vital cost effective tool in the clean up of such hazardous waste sites. Monitored Natural Attenuation (MNA) resulting from bacterial dechlorinating consortia in the groundwater community is often used as a strategy for cleaning up chlorinated solvent plumes in ground water aquifer. On the other hand, mixed microbial containing microbes like Dehalobacter spp. are added to the groundwater aquifers along with an electron donor in order to induce reductive dechlorination in a process called as bioaugmentation (14). Because of their unique metabolic properties Dehalobacter spp. are uniquely suited for bioaugmentation at sites where PCE, TCE and DCM comingle. As a result several commercial vendors have developed trademarked reductive dechlorinating cultures that contain several different strains of Dehalobacter and Dehalococcoides spp. (4, 8).
