Spain J C
Armstrong Laboratory, US Air Force, AL/EQC, Tyndall AFB, Florida 32403, USA.
Annu Rev Microbiol. 1995;49:523-55. doi: 10.1146/annurev.mi.49.100195.002515.
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.
硝基芳香化合物几乎完全是从人为来源释放到生物圈中的。一些化合物是由化石燃料不完全燃烧产生的;其他的则用作合成中间体、染料、农药和炸药。最近的研究发现了许多能够转化或生物降解硝基芳香化合物的微生物系统。厌氧细菌可以通过亚硝基和羟氨基中间体将硝基还原为相应的胺。脱硫弧菌属的分离株可以利用硝基芳香化合物作为其氮源。它们还可以将2,4,6-三硝基甲苯还原为2,4,6-三氨基甲苯。几种梭菌菌株可以催化类似的还原反应,并且似乎还能够将该分子降解为小的脂肪酸。厌氧系统已被证明可以在土壤中销毁弹药和农药。真菌可以广泛地降解或矿化各种硝基芳香化合物。例如,黄孢原毛平革菌可以将2,4-二硝基甲苯和2,4,6-三硝基甲苯矿化,并有望作为生物修复策略的基础。上述厌氧细菌和真菌大多通过偶然反应转化硝基芳香化合物。相比之下,许多硝基芳香化合物可以作为好氧细菌的生长底物。硝基的去除或有效代谢可以通过四种不同的策略来完成。(a) 一些细菌可以通过添加氢离子来还原二硝基和三硝基化合物的芳香环,形成氢化物-迈森海默络合物,随后该络合物通过消除亚硝酸盐而重新芳构化。(b) 单加氧酶可以添加一个氧原子并从硝基酚中消除硝基。(c) 双加氧酶可以将两个羟基插入芳香环,并促使各种硝基芳香化合物自发消除硝基。(d) 将硝基还原为相应的羟胺是硝基苯、4-硝基甲苯和4-硝基苯甲酸酯有效代谢的初始反应。羟胺经过酶催化重排形成羟基化化合物,这些化合物是环裂解反应的底物。上述反应的潜在应用不仅包括环境污染物的生物降解,还包括生物催化和有价值有机分子的合成。