Enzyme and Microbial Technology 37 (2005) 527–533 Biotransformation of nitroaromatics and their effects on mixed function oxidase system I. Soojhawon, P.D. Lokhande, K.M. Kodam, K.R. Gawai Department of Chemistry, University of Pune, Pune 411 007, India Received 5 October 2004; accepted 31 March 2005 Abstract Acinetobacter junii A8 was able to biotransform nitroaromatic compounds like o-nitroaniline, o-nitrotoluene, m-nitrotoluene, 2,4,6- trinitrotoluene and o-nitrophenol under aerobic condition, within 36 h of incubation. These compounds, which are normally considered to be toxic to microorganisms, caused the induction of drug metabolizing enzymes such as cytochrome P-450, aminopyrine N-demethylase, acetanilide hydroxylase and glutathione S-transferase. These enzymes constitute the bacterial mixed function oxidase system. Induction of this system implies its involvement in biotransformation of these nitro compounds. The biotransformed metabolites were characterized by IR, 1 H NMR and GC–mass spectroscopy. It was observed that o-nitroaniline and m-nitrotoluene were reduced to their respective amines, whereas o-nitrotoluene was oxidized to acid. However, 2,4,6-trinitrotoluene (TNT) and o-nitrophenol were completely mineralized. The metabolites of TNT biotransformation were characterized as 2,6-dinitro-4-nitrosotoluene, 4-amino-2,6-dinitrotoluene and 4-amino-2,6-dinitrobenzoic acid. The result of this study showed that these nitroaromatics induced the mixed function oxidase system, which resulted in the degradation of these compounds. © 2005 Elsevier Inc. All rights reserved. Keywords: Mixed function oxidase system; Biotransformation; Acinetobacter junii A8; Nitroaromatics; Cytochrome P-450 1. Introduction Nitroaromatics are important priority pollutants entering the environment primarily through anthropogenic activities associated with the industrial production of dyes, explosives, pesticides and pharmaceuticals [1,2]. Discharge of these compounds into the environment poses serious health haz- ards as they are mutagenic and bioaccumulate in the food chain [3–5]. Most of the nitroaromatics are potent uncou- plers of oxidative and photosynthetic phosphorylation [6]. The toxicity of these compounds and their recalcitrant na- ture can prove to be problematic for their effective biological treatment [7]. Moreover, aromatic compounds with multiple nitro substituents are known to be resistant to electrophilic attack by oxygenases [8]. These compounds are readily re- duced by anaerobic consortia to their respective amines [9]. However, very often, the amines are not metabolized further Corresponding author. Tel.: +91 20 25691728; fax: +91 20 25691728. E-mail address: iswarduth8@yahoo.co.uk (K.R. Gawai). under anaerobic conditions [7]. Thus, a sequential anaerobic and aerobic condition is proposed for the degradation of ni- tro aromatic compounds [10]. The biotransformation of these chemicals is carried by a group of enzymes, which is termed as mixed function oxidase system. Cytochrome P-450 is the main component of the mixed function oxidase system, which is of great catalytic versatil- ity, found in animals, plants and microorganisms. It plays an important role in the biotransformation of a wide va- riety of xenobiotics [11]. Several strains of microorgan- isms such as Streptomyces carbophilus, Rhodotorula minuta, Bacillus megaterium, Pseudomonas putida, Candida mal- tosa, etc. are known to contain cytochrome P-450 proteins [12–14]. Cytochrome P-450 typically catalyzes the monoxy- genation reaction of non-polar substrates in the presence of oxygen and two reducing equivalents [15]. Microbial cy- tochrome P-450 plays a key role in the biodegradation of a wide variety of contaminants, such as pesticides, polycyclic aromatic hydrocarbons, nitroaromatics, etc. [16–18]. Be- sides cytochrome P-450 proteins, enzymes like demethylase, 0141-0229/$ – see front matter © 2005 Elsevier Inc. All rights reserved. doi:10.1016/j.enzmictec.2005.03.011