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Aerobic dechlorination of cis- and trans-dichloroethenes by some indigenous bacteria isolated from contaminated sites in Africa 被引量:2

Aerobic dechlorination of cis- and trans-dichloroethenes by some indigenous bacteria isolated from contaminated sites in Africa
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摘要 The innate toxicity of dichloroethenes(DCEs) and their tendency to be reduced to vinyl chloride(VC)(a known human carcinogen) is a cause for environmental concern. Aerobic bacteria capable of growth on cis- and trans-DCEs as sole carbon and energy sources were isolated by enrichment culture technique and identified to belong to the genera; Bacillus, Pseudomonas and Acinetobacter. Axenic and mixed cultures of the bacterial isolates utilized DCEs at concentrations above the maximum contaminant level allowable in drinking water by the Environmental Protection Agency. Their specific growth rate constant ranged significantly(P<0.05) between 0.346—0.552 and 0.461—0.667 d -1; while the maximum specific substrate utilization rate ranged significantly(P<0.05) between 20.01—29.79 and 31.40—42.83 nmol h -1 (mg of protein) -1 in cis- and trans-DCE, respectively. The optimum growth was observed at 30℃ and at a pH of 7.0 with up to 96% of the stoichiometric-expected chloride released. Serial adaptation positively affected the growth yields and dehalogenase activities of the organisms with multiple antibiotic patterns also demonstrated by the isolates. These findings therefore indicated the important roles that these organisms may play in the bioremediation of sites polluted with chlorinated ethene compounds in Africa. The innate toxicity of dichloroethenes(DCEs) and their tendency to be reduced to vinyl chloride(VC)(a known human carcinogen) is a cause for environmental concern. Aerobic bacteria capable of growth on cis- and trans-DCEs as sole carbon and energy sources were isolated by enrichment culture technique and identified to belong to the genera; Bacillus, Pseudomonas and Acinetobacter. Axenic and mixed cultures of the bacterial isolates utilized DCEs at concentrations above the maximum contaminant level allowable in drinking water by the Environmental Protection Agency. Their specific growth rate constant ranged significantly(P<0.05) between 0.346—0.552 and 0.461—0.667 d -1; while the maximum specific substrate utilization rate ranged significantly(P<0.05) between 20.01—29.79 and 31.40—42.83 nmol h -1 (mg of protein) -1 in cis- and trans-DCE, respectively. The optimum growth was observed at 30℃ and at a pH of 7.0 with up to 96% of the stoichiometric-expected chloride released. Serial adaptation positively affected the growth yields and dehalogenase activities of the organisms with multiple antibiotic patterns also demonstrated by the isolates. These findings therefore indicated the important roles that these organisms may play in the bioremediation of sites polluted with chlorinated ethene compounds in Africa.
出处 《Journal of Environmental Sciences》 SCIE EI CAS CSCD 2004年第6期968-972,共5页 环境科学学报(英文版)
关键词 AEROBIC BIOREMEDIATION dichloroethenes DEHALOGENASE polluted site aerobic bioremediation dichloroethenes dehalogenase polluted site
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  • 1[1]Alexander M, Snow K M, 1989. Reactions and movements of organic chemicals in soils[M].In: Soil science society of America(Sawhney B.L., Brown K. ed.). Madison,Wisconsin, WI. 243-269.
  • 2[2]Beeman R E, Howell J E, Shoemaker S H et al., 1994. A field evaluation of in situ microbial reductive dehalogenation by transformation of chlorinated ethylenes[M]. In: Bioremediation of chlorinated and polycyclic aromatic hydrocarbon compounds(Hinchee R.E., Leeson A., Semprini L., Ong S.K. ed.). Boca Raton, Fla: Lewis Publishers. 14-27.
  • 3[3]Bergmann J G, Sanik J, 1957. Determination of trace amounts of chlorine in naphtha[J]. Analytical Chemistry, 29: 241-243.
  • 4[4]Biswas N, 1992. Model for predicting PCE desorption from contaminated soils[J]. Water Environ Res, 64: 170.
  • 5[5]Bolesch D, Nielsen R, Keasling J, 1997. Complete reductive dechlorination of trichloroethene by a ground water microbial consortium[J]. Ann NY Acad Sci, 829: 97-102.
  • 6[6]Bouchez M, Blanchet D, Vandecasteele J P, 1995. Degradation of polycyclic aromatic hydrocarbons by pure strains and by defined strain associations: inhibition phenomena and cometabolism[J]. Applied Microbiology and Biotechnology, 43: 156-164.
  • 7[7]Bouwer E J, 1994. Bioremediation of chlorinated solvents using alternate electron acceptors[J]. In: Handbook of bioremediation((Norris R.D., Hinchee R.E., Brown R. et al., ed.). Boca Raton: Lewis Publishers. 177-199.
  • 8[8]Bradley P M, Chapelle F H, 1996. Anaerobic mineralization of vinyl chloride in Fe(III)-reducing aquifer sediments[J]. Environ Sci Technol, 30: 2692-2696.
  • 9[9]Bradley P M, Chapelle F H, 1998a. Effect of contaminant concentration on aerobic microbial mineralization of DCE and VC in stream-bed sediments[J]. Environ Sci Technol, 32: 553-557.
  • 10[10]Bradley P M, Chapelle F H, 2000. Aerobic microbial mineralization of dichloroethene as sole carbon substrate[J]. Environ Sci Technol, 34: 221-223.

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