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Obligately Anaerobic Bacteria in Biotechnology

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Date 1994 Aug 1
PMID 7944353
Citations 2
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Abstract

New obligately anaerobic bacteria are being discovered at an accelerating rate and it is becoming very evident that the diversity of anoxic biotransformations has been greatly underestimated. Furthermore, among contemporary anaerobes there are many that thrive in extreme environments including, for example, an impressive array of both archaebacterial and eubacterial hyperthermophiles. Free energy for growth and reproduction may be conserved not only via fermentations but also by anoxygenic photophosphorylation and other modes of creating transmembrane proton potential. Thus forms of anaerobic respiration in which various inorganic oxidants (or indeed carbon dioxide) serve as terminal electron acceptors have greatly extended the natural habitats in which such organisms may predominate. Anaerobic bacteria are, however, often found in nature as members of close microbial communities (consortia) that, although sustained by syntrophic and other relations between component species, are liable to alter their composition and character in response to environmental changes, e.g., availability of terminal oxidants. It follows that the biotechnological exploitation of obligately anaerobic bacteria must be informed by knowledge both of their biochemical capacities and of their normal environmental roles. It is against this background that illustrative examples of the activities of anaerobic bacteria are considered under three heads: 1. Biodegradation/Bioremediation, with special reference to the anaerobic breakdown of aromatic and/or halogenated organic substances; 2. Biosynthesis/Bioproduction, encompassing normal and modified fermentations; and 3. Biotransformations, accomplished by whole or semipermeabilized organisms or by enzymes derived therefrom, with particular interest attaching to the production of chiral compounds by a number of procedures, including electromicrobial reduction.

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References
1.
Hopper D, Bossert I . p-cresol methylhydroxylase from a denitrifying bacterium involved in anaerobic degradation of p-cresol. J Bacteriol. 1991; 173(3):1298-301. PMC: 207254. DOI: 10.1128/jb.173.3.1298-1301.1991. View

2.
White H, Feicht R, Huber C, Lottspeich F, Simon H . Purification and some properties of the tungsten-containing carboxylic acid reductase from Clostridium formicoaceticum. Biol Chem Hoppe Seyler. 1991; 372(11):999-1005. DOI: 10.1515/bchm3.1991.372.2.999. View

3.
Williams R, Evans W . The metabolism of benzoate by Moraxella species through anaerobic nitrate respiration. Evidence for a reductive pathway. Biochem J. 1975; 148(1):1-10. PMC: 1165499. DOI: 10.1042/bj1480001a. View

4.
Wu W, Bhatnagar L, Zeikus J . Performance of anaerobic granules for degradation of pentachlorophenol. Appl Environ Microbiol. 1993; 59(2):389-97. PMC: 202117. DOI: 10.1128/aem.59.2.389-397.1993. View

5.
Rabus R, Nordhaus R, Ludwig W, Widdel F . Complete oxidation of toluene under strictly anoxic conditions by a new sulfate-reducing bacterium. Appl Environ Microbiol. 1993; 59(5):1444-51. PMC: 182102. DOI: 10.1128/aem.59.5.1444-1451.1993. View