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The anaerobic biodegradation of 2,4,5-trichlorophenoxyacetic acid (2,4,5-T) was investigated using enrichment cultures from freshwater sediments at two different sites in the region of Halle, central Germany. 2,4,5-T and different organic acids or hydrogen were added as possible electron acceptor and electron donors, respectively. The primary enrichment cultures from Saale river sediment completely degraded 2,4,5-T to 3-chlorophenol (3-CP) (major product) and 3,4-dichlorophenol (3,4-DCP) during a 28-day incubation period. Subcultures showed ether cleavage of 2,4,5-T to 2,4,5-trichlorophenol and its stoichiometric dechlorination to 3-CP only in the presence of butyrate. In contrast, the primary enrichment culture from sediment of Posthorn pond dechlorinated 2,4,5-T to 2,5-dichlorophenoxyacetic acid (2,5-D), which, in the presence of butyrate, was degraded further to products such as 3,4-DCP, 2,5-DCP, and 3CP, indicating ether cleaving activities and subsequent dechlorination steps. Experiments with pure cultures of Dehalococcoides mccartyi and Desulfitobacterium hafniense demonstrated their specific dechlorination steps within the overall 2,4,5-T degradation pathways. The results indicate that the route and efficiency of anaerobic 2,4,5-T degradation in the environment depend heavily on the microorganisms present and the availability of slowly fermentable organic compounds.

The herbicide 2,4,5‐trichlorophenoxyacetic acid (2,4,5‐T) was a major component of Agent Orange, which was used as a defoliant in the Vietnam War. Little is known about its degradation under anoxic conditions. Established enrichment cultures using soil from an Agent Orange bioremediation plant in southern Vietnam with pyruvate as potential electron donor and carbon source were shown to degrade 2,4,5‐T via ether cleavage to 2,4,5‐trichlorophenol (2,4,5‐TCP), which was further dechlorinated to 3,4‐dichlorophenol. Pyruvate was initially fermented to hydrogen, acetate and propionate. Hydrogen was then used as the direct electron donor for ether cleavage of 2,4,5‐T and subsequent dechlorination of 2,4,5‐TCP. 16S rRNA gene amplicon sequencing indicated the presence of bacteria and archaea mainly belonging to the Firmicutes, Bacteroidetes, Spirochaetes, Chloroflexi and Euryarchaeota. Desulfitobacterium hafniense was identified as the dechlorinating bacterium. Metaproteomics of the enrichment culture indicated higher protein abundances of 60 protein groups in the presence of 2,4,5‐T. A reductive dehalogenase related to RdhA3 of D. hafniense showed the highest fold change, supporting its function in reductive dehalogenation of 2,4,5‐TCP. Despite an ether‐cleaving enzyme not being detected, the inhibition of ether cleavage but not of dechlorination, by 2‐bromoethane sulphonate, suggested that the two reactions are catalysed by different organisms.

The megasite Bitterfeld-Wolfen is highly contaminated as a result of accidents and because of dumping of wastes from local chemical industries in the last century. A variety of contaminants including chlorinated ethenes and benzenes, hexachlorohexanes and chlorinated dioxins can still be found in the groundwater and (river) sediments. Investigations of the in situ microbial transformation of organohalides have been performed only over the last two decades at this megasite. In this review, we summarise the research on the activity of anaerobic dehalogenating bacteria at the field site in Bitterfeld-Wolfen, focusing on chlorinated ethenes, monochlorobenzene and chlorinated dioxins. Various methods and concepts were applied including ex situ cultivation and isolation, and in situ analysis of hydrochemical parameters, compound-specific stable isotope analysis of contaminants, 13C-tracer studies and molecular markers. Overall, biotransformation of organohalides is ongoing at the field site and Dehalococcoides mccartyi species play an important role in the detoxification process in the Bitterfeld-Wolfen region.

Dehalococcoides mccartyi is a small, slow-growing bacterium of the phylum Chloroflexi that conserves energy using aliphatic and aromatic organohalides as electron acceptors, and hydrogen as sole electron donor. A recent study identified a protein complex in the membrane of strain CBDB1 comprising a Hup hydrogenase, a complex iron-sulphur molybdoprotein and a reductive dehalogenase (RdhA) that catalyses reduction of 1,2,3,4-tetrachlorobenzene. Using a combination of size-exclusion chromatography, in-gel hydrogenase activity-staining, immunological analysis and mass spectrometry, we identified here a large molecular mass protein complex solubilized from the cytoplasmic membrane of D. mccartyi strain CBDB1 that catalysed H2-dependent reduction of 1,2,3-trichlorobenzene (1,2,3-TCB) to 1,3-DCB. In-gel zymographic staining revealed H2:benzyl viologen oxidoreductase activity associated with the complex and immunological analysis identified co-elution of CdbdA195, the predicted catalytic subunit of the iron-sulphur molybdoenzyme, the chlorobenzene-specific RdhA, CbrA, and traces of HupL, the catalytic subunit of the Hup hydrogenase. Quantitative reverse transcriptase PCR analyses indicated that the expression of the hupL and cbdbA195 genes was induced by 1,2,3-TCB but not by hydrogen. Together, these data identify and describe a protein-based electron-transfer complex catalysing H2 oxidation coupled to chlorobenzene reduction.

Zusammenfassung: Die neuen, mit Mitteln der Informations- und Kommunikationstechnologie geschaffenen Medien, insbesondere Medien zur Organisation der wirtschaftlichen Leistungserstellung, sind Plattformen für weltweite Gemeinschaften und induzieren neuartige Gemeinschaften. Unser Ansatz betrachtet Medien ganzheitlich, d.h. die Plattformen und ihre Gemeinschaften und stellt dabei die Gemeinschaft mit ihren Anforderungen in das Zentrum der neuen Medien. Wir zeigen verschiedene Gemeinschaften in diesen Medien auf, charakterisieren und modellieren sie und entwickeln Ansätze zum Management dieser Gemeinschaften in und mit den neuen Medien.

Reductive dehalogenases are essential enzymes in organohalide respiration and consist of a catalytic subunit A and a membrane protein B, encoded by rdhAB genes. Thirty-two rdhAB genes exist in the genome of Dehalococcoides mccartyi strain CBDB1. To gain a first insight into the regulation of rdh operons, the control of gene expression of two rdhAB genes (cbdbA1453/cbdbA1452 and cbdbA1455/cbdbA1454) by the MarR-type regulator Rdh2R (cbdbA1456) encoded directly upstream was studied using heterologous expression and in vitro studies. Promoter-lacZ reporter fusions were generated and integrated into the genome of the Escherichia coli host. The lacZ reporter activities of both rdhA promoters decreased upon transformation of the cells with a plasmid carrying the rdh2R gene, suggesting that Rdh2R acts as repressor, whereas the lacZ reporter activity of the rdh2R promoter was not affected. The transcriptional start sites of both rdhA genes in strain CBDB1 and/or the heterologous host mapped to a conserved direct repeat with 11- to 13-bp half-sites. DNase I footprinting revealed binding of Rdh2R to a ∼30-bp sequence covering the complete direct repeat in both promoters, including the transcriptional start sites. Equilibrium sedimentation ultracentrifugation revealed that Rdh2R binds as tetramer to the direct-repeat motif of the rdhA (cbdbA1455) promoter. Using electrophoretic mobility shift assays, a similar binding affinity was found for both rdhA promoters. In the presence of only one half-site of the direct repeat, the interaction was strongly reduced, suggesting a positive cooperativity of binding, for which unusual short palindromes within the direct-repeat half-sites might play an important role. IMPORTANCE Dehalococcoides mccartyi strains are obligate anaerobes that grow by organohalide respiration. They have an important bioremediation potential because they are capable of reducing a multitude of halogenated compounds to less toxic products. We are now beginning to u

Polyhalogenated aromatic compounds are harmful environmental contaminants and tend to persist in anoxic soils and sediments. Dehalococcoides mccartyi strain DCMB5, a strain originating from dioxin-polluted river sediment, was examined for its capacity to dehalogenate diverse chloroaromatic compounds. Strain DCMB5 used hexachlorobenzenes, pentachlorobenzenes, all three tetrachlorobenzenes, and 1,2,3-trichlorobenzene as well as 1,2,3,4-tetra- and 1,2,4-trichlorodibenzo-p-dioxin as electron acceptors for organohalide respiration. In addition, 1,2,3-trichlorodibenzo-p-dioxin and 1,3-, 1,2-, and 1,4-dichlorodibenzo-p-dioxin were dechlorinated, the latter to the nonchlorinated congener with a remarkably short lag phase of 1 to 4 days following transfer. Strain DCMB5 also dechlorinated pentachlorophenol and almost all tetra- and trichlorophenols. Tetrachloroethene was dechlorinated to trichloroethene and served as an electron acceptor for growth. To relate selected dechlorination activities to the expression of specific reductive dehalogenase genes, the proteomes of 1,2,3-trichlorobenzene-, pentachlorobenzene-, and tetrachloroethene-dechlorinating cultures were analyzed. Dcmb_86, an ortholog of the chlorobenzene reductive dehalogenase CbrA, was the most abundant reductive dehalogenase during growth with each electron acceptor, suggesting its pivotal role in organohalide respiration of strain DCMB5. Dcmb_1041 was specifically induced, however, by both chlorobenzenes, whereas 3 putative reductive dehalogenases, Dcmb_1434, Dcmb_1339, and Dcmb_1383, were detected only in tetrachloroethene-grown cells. The proteomes also harbored a type IV pilus protein and the components for its assembly, disassembly, and secretion. In addition, transmission electron microscopy of DCMB5 revealed an irregular mode of cell division as well as the presence of pili, indicating that pilus formation is a feature of D. mccartyi during organohalide respiration.

The genomes of two novel Dehalococcoides mccartyi strains, DCMB5 and BTF08, enriched from the heavily organohalide-contaminated megasite around Bitterfeld (Germany), were fully sequenced and annotated. Although overall similar, the genome sequences of the two strains reveal remarkable differences in their genetic content, reflecting a specific adaptation to the contaminants at the field sites from which they were enriched. The genome of strain BTF08 encodes for 20 reductive dehalogenases, including all three of which are necessary to couple the reductive dechlorination of PCE to ethene to growth. The genes encoding trichloroethene and vinyl chloride reductive dehalogenases, tceA and vcrA, are located within mobile genetic elements, suggesting their recent horizontal acquisition. The genome of strain DCMB5 contains 23 reductive dehalogenase genes, including cbrA, which encodes a chlorobenzene reductive dehalogenase, and a gene cluster encoding arsenic resistance proteins, both corresponding to typical pollutants at its isolation site.

The transcription of reductive dehalogenase homologous (rdh) genes of "Dehalococcoides" sp. strain CBDB1 was investigated during the growth and reductive dechlorination of 1,2,3- and 1,2,4-trichlorobenzene (TCB). A method was developed to monitor the expression of all 32 rdhA genes present in the genome based on reverse transcription-PCR amplification with 13 degenerate primer pairs and terminal restriction fragment length polymorphism (t-RFLP) analysis. With this approach, the upregulation of the transcription of 29 rdhA genes was indicated in response to 1,2,3- and 1,2,4-TCB added after a substrate depletion period of 72 h. The transcription of the remaining three rdhA genes additionally was detected using specific primers. While most rdhA genes were upregulated similarly in cultures after induction with 1,2,3-TCB or 1,2,4-TCB, three rdhA genes responded differentially to 1,2,3- and 1,2,4-TCB, as revealed by the comparison of t-RFLP profiles. The enhanced transcription of cbdbA1453 and cbdbA187 was observed in the presence of 1,2,3-TCB, while the transcription of cbdbA1624 was strongly induced by 1,2,4-TCB. Comparison of t-RFLP profiles obtained from cDNA and genomic DNA indicated a particularly high induction of the transcription of cbrA (=cbdbA84) by both TCBs. As indicated by reverse transcription-quantitative PCR, the transcription of these plus two other rdhA genes (cbdbA1588 and cbdbA1618) increased within 48 to 72 h by one or two orders of magnitude. Subsequently, transcript levels slowly decreased and approached initial transcript levels several days after complete dehalogenation. Finally, cbrA was transcribed to a level of 22 transcripts per cbrA gene, suggesting that cbrA mRNA could be an appropriate biomarker for the investigation of the natural dechlorination potential at chlorobenzene-contaminated sites.

Strains L10T, L108 and CIP I-2052 were originally obtained from methyl tert-butyl ether (MTBE)-contaminated groundwater and from a wastewater treatment plant, respectively. All share the ability to grow on tert-butanol, an intermediate of MTBE degradation. Cells are strictly aerobic, motile by a polar flagellum and exhibit strong pili formation. Poly -hydroxybutyrate (PHB) granules are formed. The DNA G+C content is 69-70.5 mol% and the main ubiquinone is Q-8. The major cellular fatty acids are 16 : 1 cis-9 and 16 : 0 and the only hydroxy fatty acid is 10 : 0 3-OH. The major phospholipids are phosphatidylethanolamine (PE) 16 : 1/16 : 1 and phosphatidylglycerol 16 : 0/16 : 1. A significant amount of PE 17 : 0/16 : 1 is present. The 16S rRNA gene sequences of these strains are almost identical and form a separate line of descent in the Rubrivivax-Roseateles-Leptothrix-Ideonella-Aquabacterium branch of the Betaproteobacteria with 97 % similarity to 16S rRNA genes of the type strains of Rubrivivax gelatinosus, Leptothrixmobilis and Ideonella dechloratans. However, physiological properties, DNA-DNA relatedness values and the phospholipid and cellular fatty acid profiles distinguish the novel isolates from the three closely related genera. Therefore, it is concluded that strains L10T, L108 and CIP I-2052 represent a new genus and novel species for which the name Aquincola tertiaricarbonis gen. nov., sp. nov., is proposed. The type strain is strain L10T (=DSM 18512T=CIP 109243T).

An anaerobic enrichment culture reductively dehalogenated 1,2,4- and 1,2,3-trichlorodibenzo-p-dioxin (TrCDD) almost exclusively at peripheral positions forming the main products 1,3-dichloro-(DiCDD) and 2-monochlorodibenzo-p-dioxin (MCDD) from 1,2,4-TrCDD and 2,3-DiCDD from 1,2,3-TrCDD. Dehalococcoides was monitored in the mixed culture by quantitative real-time PCR. A yield of 2.5 × 108 to 2.75 × 108 copies of 16S rRNA genes per micromole of chloride released suggested growth by dehalorespiration with dibenzo-p-dioxins. For the analysis of carbon isotope fractionation, the dioxin congeners were isolated by solid-phase microextraction (SPME) from the headspace of the cultures. The 13C composition of 1,2,4-TrCDD did not change remarkably during the course of reductive dehalogenation; however, the intermediate 1,3-DiCDD became enriched, and the final product 2-MCDD significantly depleted in 13C with a discrimination of 2.5-3.6" between 1,3-DiCDD and 2-MCDD. 1,2,3-TrCDD and its main product 2,3-DiCDD became slightly enriched in 13C, whereas the formed low concentrations of 2-MCDD were depleted in 13C by 5.5-4.8". This study demonstrates carbon isotope fractionation during sequential reductive dehalogenation of chlorinated dibenzo-p-dioxins, whereby isotope fractionation upon dehalogenation of the intermediate was substantial. This can provide a basis for the development of a new method to monitor the fate of dioxins in the environment using compound specific stable isotope analyses.

Fuel oxygenates such as methyl and ethyl tert-butyl ether (MTBE and ETBE, respectively) are degraded only by a limited number of bacterial strains. The aerobic pathway is generally thought to run via tert-butyl alcohol (TBA) and 2-hydroxyisobutyrate (2-HIBA), whereas further steps are unclear. We have now demonstrated for the newly isolated ß-proteobacterial strains L108 and L10, as well as for the closely related strain CIP I-2052, that 2-HIBA was degraded by a cobalamin-dependent enzymatic step. In these strains, growth on substrates containing the tert-butyl moiety, such as MTBE, TBA, and 2-HIBA, was strictly dependent on cobalt, which could be replaced by cobalamin. Tandem mass spectrometry identified a 2-HIBA-induced protein with high similarity to a peptide whose gene sequence was found in the finished genome of the MTBE-degrading strain Methylibium petroleiphilum PM1. Alignment analysis identified it as the small subunit of isobutyryl-coenzyme A (CoA) mutase (ICM; EC 5.4.99.13), which is a cobalamin-containing carbon skeleton-rearranging enzyme, originally described only in Streptomyces spp. Sequencing of the genes of both ICM subunits from strain L108 revealed nearly 100% identity with the corresponding peptide sequences from M. petroleiphilum PM1, suggesting a horizontal gene transfer event to have occurred between these strains. Enzyme activity was demonstrated in crude extracts of induced cells of strains L108 and L10, transforming 2-HIBA into 3-hydroxybutyrate in the presence of CoA and ATP. The physiological and evolutionary aspects of this novel pathway involved in MTBE and ETBE metabolism are discussed.

Strain ZF2T, isolated from freshwater sediment, is a motile, rod-shaped, gram-positive, endospore-forming, amino acid- and pyruvate-utilizing, anaerobic bacterium. It requires yeast extract for growth. Carbohydrates are not utilized. The optimal temperature and pH for growth are 37 degrees C and 6.8-7.3, respectively. The G+C content of the DNA is 34.0 mol %. A 16S rDNA sequence analysis of strain ZF2T revealed that the highest similarity (94.4%) was shared with Clostridium hydroxybenzoicum JW/Z-1T. Strain ZF2T, however, was not able to carboxylate phenol or to decarboxylate 4-hydroxybenzoate, which are characteristic properties of strain JW/Z-1T. The degree of 16S rDNA relatedness, together with the physiological and chemotaxonomic properties, suggest that strain ZF2T represents a novel species that is clearly distinct from Clostridium hydroxybenzoicum JW/Z-1T. In a phylogenetic dendrogram, both strains form a separate cluster that is peripherally associated with the Peptostreptococcus group (cluster XIII) of the clostridia and the lineage of Helcococcus kunzii. Strains ZF2T and JW/Z-1T show a somewhat deeper branching from the cluster XII clostridia Clostridium purinolyticum and Clostridium acidiurici. The latter strains possessed the closest 16S rDNA similarity (between 88.4 and 90.7%), but were clearly separated by phenotypic markers. Therefore, a new genus, Sedimentibacter gen. nov., is described, comprising Sedimentibacter hydroxybenzoicus gen. nov., comb. nov., as the type species of the genus, with JW/Z-1T (= ATCC 51151T = DSM 7310T) as the type strain, and the novel species Sedimentibacter saalensis sp. nov., with strain ZF2T (= DSM 13558T = ATCC BAA-283T) as the type strain.