Biochemistry, Physiology and Biotechnology of Sulfate-Reducing Bacteria

被引:260
|
作者
Barton, Larry L. [1 ]
Fauque, Guy D. [2 ,3 ,4 ]
机构
[1] Univ New Mexico, Dept Biol, Albuquerque, NM 87131 USA
[2] Univ Aix Marseille 1, UMR 180, Lab Microbiol IRD, F-13288 Marseille 09, France
[3] Univ Mediterranee, ESIL GBMA, F-13288 Marseille 09, France
[4] CNRS, Lab Microbiol Geochim & Ecol Marines, URM 6117, F-13288 Marseille 09, France
关键词
DESULFOVIBRIO-DESULFURICANS ATCC-27774; DESULFITOBACTERIUM-FRAPPIERI TCE1; EXTRACELLULAR ELECTRON-TRANSFER; GENE-EXPRESSION ANALYSIS; SPIN SULFITE REDUCTASE; C NITRITE REDUCTASE; 9-HEME CYTOCHROME-C; VULGARIS HILDENBOROUGH; SP-NOV; ANAEROBIC DEGRADATION;
D O I
10.1016/S0065-2164(09)01202-7
中图分类号
Q81 [生物工程学(生物技术)]; Q93 [微生物学];
学科分类号
071005 ; 0836 ; 090102 ; 100705 ;
摘要
Chemolithotrophic bacteria that use sulfate as terminal electron acceptor (sulfate-reducing bacteria) constitute a unique physiological group of microorganisms that couple anaerobic electron transport to ATP synthesis. These bacteria (220 species of 60 genera) can use a large variety of compounds as electron donors and to mediate electron flow they have a vast array of proteins with redox active metal groups. This chapter deals with the distribution in the environment and the major physiological and metabolic characteristics of sulfate-reducing bacteria (SRB). This chapter presents our current knowledge of soluble electron transfer proteins and transmembrane redox complexes that are playing an essential role in the dissimilatory sulfate reduction pathway of SRB of the genus Desulfovibrio. Environmentally important activities displayed by SRB are a consequence of the unique electron transport components or the production of high levels of H2S. The capability of SRB to utilize hydrocarbons in pure cultures and consortia has resulted in using these bacteria for bioremediation of BTEX (benzene, toluene, ethylbenzene and xylene) compounds in contaminated soils. Specific strains of SRB are capable of reducing 3-chlorobenzoate, chloroethenes, or nitroaromatic compounds and this has resulted in proposals to use SRB for bioremediation of environments containing trinitrotoluene and polychloroethenes. Since SRB have displayed dissimilatory reduction of U(VI) and Cr(VI), several biotechnology procedures have been proposed for using SRB in bioremediation of toxic metals. Additional non-specific metal reductase activity has resulted in using SRB for recovery of precious metals (e.g. platinum, palladium and gold) from waste streams. Since bacterially produced sulfide contributes to the souring of oil fields, corrosion of concrete, and discoloration of stonework is a serious problem, there is considerable interest in controlling the sulfidogenic activity of the SRB. The production of biosulfide by SRB has led to immobilization of toxic metals and reduction of textile dyes, although the process remains unresolved, SRB play a role in anaerobic methane oxidation which not only contributes to carbon cycle activities but also depletes an important industrial energy reserve.
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页码:41 / 98
页数:58
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