Biotransformation of Hexahydro-1,3,5-Trinitro-1,3,5-Triazine (RDX) by a Rabbit Liver Cytochrome P450: Insight into the Mechanism of RDX Biodegradation by Rhodococcus sp. Strain DN22

ABSTRACT A unique metabolite with a molecular mass of 119 Da (C2H5N3O3) accumulated during biotransformation of hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX) by Rhodococcus sp. strain DN22 (D. Fournier, A. Halasz, J. C. Spain, P. Fiurasek, and J. Hawari, Appl. Environ. Microbiol. 68:166-172, 2002). The structure of the molecule and the reactions that led to its synthesis were not known. In the present study, we produced and purified the unknown metabolite by biotransformation of RDX with Rhodococcus sp. strain DN22 and identified the molecule as 4-nitro-2,4-diazabutanal using nuclear magnetic resonance and elemental analyses. Furthermore, we tested the hypothesis that a cytochrome P450 enzyme was responsible for RDX biotransformation by strain DN22. A cytochrome P450 2B4 from rabbit liver catalyzed a very similar biotransformation of RDX to 4-nitro-2,4-diazabutanal. Both the cytochrome P450 2B4 and intact cells of Rhodococcus sp. strain DN22 catalyzed the release of two nitrite ions from each reacted RDX molecule. A comparative study of cytochrome P450 2B4 and Rhodococcus sp. strain DN22 revealed substantial similarities in the product distribution and inhibition by cytochrome P450 inhibitors. The experimental evidence led us to propose that cytochrome P450 2B4 can catalyze two single electron transfers to RDX, thereby causing double denitration, which leads to spontaneous hydrolytic ring cleavage and decomposition to produce 4-nitro-2,4-diazabutanal. Our results provide strong evidence that a cytochrome P450 enzyme is the key enzyme responsible for RDX biotransformation by Rhodococcus sp. strain DN22.

[1]  J. Hawari,et al.  Biodegradation of Hexahydro-1,3,5-Trinitro-1,3,5-Triazine and Its Mononitroso Derivative Hexahydro-1-Nitroso-3,5-Dinitro-1,3,5-Triazine by Klebsiella pneumoniae Strain SCZ-1 Isolated from an Anaerobic Sludge , 2002, Applied and Environmental Microbiology.

[2]  E. Travis,et al.  Cloning, Sequencing, and Characterization of the Hexahydro-1,3,5-Trinitro-1,3,5-Triazine Degradation Gene Cluster from Rhodococcus rhodochrous , 2002, Applied and Environmental Microbiology.

[3]  N. Coleman,et al.  Evidence that RDX biodegradation by Rhodococcus strain DN22 is plasmid‐borne and involves a cytochrome p‐450 , 2002, Journal of applied microbiology.

[4]  B. Bhushan,et al.  Biotransformation of hexahydro-1,3,5-trinitro-1,3,5-tiazine catalyzed by a NAD(P)H: nitrate oxidoreductase from Aspergillus niger. , 2002, Environmental science & technology.

[5]  J. Hawari,et al.  Insights into the formation and degradation mechanisms of methylenedinitramine during the incubation of RDX with anaerobic sludge. , 2002, Environmental science & technology.

[6]  J. Hawari,et al.  Determination of Key Metabolites during Biodegradation of Hexahydro-1,3,5-Trinitro-1,3,5-Triazine with Rhodococcus sp. Strain DN22 , 2002, Applied and Environmental Microbiology.

[7]  C. Just,et al.  Hexahydro-1,3,5-trinitro-1,3,5-triazine mineralization by zerovalent iron and mixed anaerobic cultures. , 2001, Environmental science & technology.

[8]  F. Guengerich,et al.  Common and uncommon cytochrome P450 reactions related to metabolism and chemical toxicity. , 2001, Chemical research in toxicology.

[9]  J. Hawari Biodegradation of RDX and HMX: From Basic Research to Field Application , 2000 .

[10]  Joseph B. Hughes,et al.  Biodegradation of Nitroaromatic Compounds and Explosives , 2000 .

[11]  J. Hawari,et al.  Characterization of Metabolites during Biodegradation of Hexahydro-1,3,5-Trinitro-1,3,5-Triazine (RDX) with Municipal Anaerobic Sludge , 2000, Applied and Environmental Microbiology.

[12]  C. Kitts,et al.  Type I Nitroreductases in Soil Enterobacteria Reduce TNT (2,4,6-Trinitrotoluene) and RDX (Hexahydro-1,3,5-Trinitro-1,3,5-Triazine) , 2000 .

[13]  D. Nelson,et al.  Aerobic biodegradation of hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX) as a nitrogen source by a Rhodococcus sp., strain DN22 , 1998 .

[14]  D. Young,et al.  Biotransformation of hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX) by a prospective consortium and its most effective isolate Serratia marcescens. , 1997, Biotechnology and bioengineering.

[15]  N. Bruce,et al.  Degradation of hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX) by Stenotrophomonas maltophilia PB1 , 1995, Applied and environmental microbiology.

[16]  K. Timmis,et al.  Two independently regulated cytochromes P-450 in a Rhodococcus rhodochrous strain that degrades 2-ethoxyphenol and 4-methoxybenzoate , 1993, Journal of bacteriology.

[17]  Ortiz de Montellano,et al.  Cytochrome P-450: Structure, Mechanism, and Biochemistry , 1986 .

[18]  J. Cornell,et al.  Biodegradation of Hexahydro-1,3,5-Trinitro-1,3,5-Triazine , 1981, Applied and environmental microbiology.

[19]  J. Owens,et al.  The nitrogen nutrition of soil and herbage coryneform bacteria. , 1969, The Journal of applied bacteriology.

[20]  F. M. Cretella,et al.  Nitroaromatic munition compounds: environmental effects and screening values. , 1999, Reviews of environmental contamination and toxicology.

[21]  C. A. Myler,et al.  Bioremediation of Explosives Contaminated Soils (Scientific Questions/Engineering Realities) , 1991 .

[22]  R. Haas,et al.  Conception for the investigation of contaminated munition plants , 1990 .