Literature DB >> 8561470

Biodegradation of nitroaromatic compounds.

J C Spain1.   

Abstract

Nitroaromatic compounds are released into the biosphere almost exclusively from anthropogenic sources. Some compounds are produced by incomplete combustion of fossil fuels; others are used as synthetic intermediates, dyes, pesticides, and explosives. Recent research revealed a number of microbial systems capable of transforming or biodegrading nitroaromatic compounds. Anaerobic bacteria can reduce the nitro group via nitroso and hydroxylamino intermediates to the corresponding amines. Isolates of Desulfovibrio spp. can use nitroaromatic compounds as their source of nitrogen. They can also reduce 2,4,6-trinitrotoluene to 2,4,6-triaminotoluene. Several strains of Clostridium can catalyze a similar reduction and also seem to be able to degrade the molecule to small aliphatic acids. Anaerobic systems have been demonstrated to destroy munitions and pesticides in soil. Fungi can extensively degrade or mineralize a variety of nitroaromatic compounds. For example, Phanerochaete chrysosporium mineralizes 2,4-dinitrotoluene and 2,4,6-trinitrotoluene and shows promise as the basis for bioremediation strategies. The anaerobic bacteria and the fungi mentioned above mostly transform nitroaromatic compounds via fortuitous reactions. In contrast, a number of nitroaromatic compounds can serve as growth substrates for aerobic bacteria. Removal or productive metabolism of nitro groups can be accomplished by four different strategies. (a) Some bacteria can reduce the aromatic ring of dinitro and trinitro compounds by the addition of a hydride ion to form a hydride-Meisenheimer complex, which subsequently rearomatizes with the elimination of nitrite. (b) Monooxygenase enzymes can add a single oxygen atom and eliminate the nitro group from nitrophenols. (c) Dioxygenase enzymes can insert two hydroxyl groups into the aromatic ring and precipitate the spontaneous elimination of the nitro group from a variety of nitroaromatic compounds. (d) Reduction of the nitro group to the corresponding hydroxylamine is the initial reaction in the productive metabolism of nitrobenzene, 4-nitrotoluene, and 4-nitrobenzoate. The hydroxylamines undergo enzyme-catalyzed rearrangements to hydroxylated compounds that are substrates for ring-fission reactions. Potential applications of the above reactions include not only the biodegradation of environmental contaminants, but also biocatalysis and synthesis of valuable organic molecules.

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Year:  1995        PMID: 8561470     DOI: 10.1146/annurev.mi.49.100195.002515

Source DB:  PubMed          Journal:  Annu Rev Microbiol        ISSN: 0066-4227            Impact factor:   15.500


  92 in total

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5.  Arabidopsis and the genetic potential for the phytoremediation of toxic elemental and organic pollutants.

Authors:  Christopher S Cobbett; Richard B Meagher
Journal:  Arabidopsis Book       Date:  2002-04-04

Review 6.  Nitroaromatic compounds, from synthesis to biodegradation.

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Journal:  Microbiol Mol Biol Rev       Date:  2010-06       Impact factor: 11.056

7.  Molecular and biochemical characterization of the 5-nitroanthranilic acid degradation pathway in Bradyrhizobium sp. strain JS329.

Authors:  Yi Qu; Jim C Spain
Journal:  J Bacteriol       Date:  2011-04-15       Impact factor: 3.490

8.  Identifying Unknown Enzyme-Substrate Pairs from the Cellular Milieu with Native Mass Spectrometry.

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9.  Sequential anaerobic-aerobic biodegradation of emerging insensitive munitions compound 3-nitro-1,2,4-triazol-5-one (NTO).

Authors:  Camila L Madeira; Samuel A Speet; Cristina A Nieto; Leif Abrell; Jon Chorover; Reyes Sierra-Alvarez; Jim A Field
Journal:  Chemosphere       Date:  2016-10-15       Impact factor: 7.086

10.  Enzymatic hydrolysis by transition-metal-dependent nucleophilic aromatic substitution.

Authors:  Sibel Kalyoncu; David P Heaner; Raquel L Lieberman; Zohre Kurt; Casey M Bethel; Chiamaka U Ukachukwu; Srinivas Chakravarthy; Jim C Spain
Journal:  Nat Chem Biol       Date:  2016-10-03       Impact factor: 15.040

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