Literature DB >> 12775055

Alkaline hydrolysis of the cyclic nitramine explosives RDX, HMX, and CL-20: new insights into degradation pathways obtained by the observation of novel intermediates.

Vimal K Balakrishnan1, Annamaria Halasz, Jalal Hawari.   

Abstract

Hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX, I) and octahydro-1,3,5,7-tetranitro-1,3,5,7-tetrazocine (n class="Chemical">HMX) hydrolyze at pH > 10 to form end products including NO2-, HCHO, HCOOH, NH3, and N2O, but little information is available on intermediates, apart from the tentatively identified pentahydro-3,5-dinitro-1,3,5-triazacyclohex-1-ene (II). Despite suggestions that RDX and HMX contaminated groundwater could be economically treated via alkaline hydrolysis, the optimization of such a process requires more detailed knowledge of intermediates and degradation pathways. In this study, we hydrolyzed the monocyclic nitramines RDX, MNX (hexahydro-1-nitroso-3,5-dinitro-1,3,5-triazine), and HMX in aqueous solution (pH 10-12.3) and found that nitramine removal was accompanied by formation of 1 molar equiv of nitrite and the accumulation of the key ring cleavage product 4-nitro-2,4-diazabutanal (4-NDAB, O2NNHCH2NHCHO). Most of the remaining C and N content of RDX, MNX, and HMX was found in HCHO, N2O, HCOOH, and NH3. Consequently, we selected RDX as a model compound and hydrolyzed it in aqueous acetonitrile solutions (pH 12.3) in the presence and absence of hydroxypropyl-beta-cyclodextrin (HP-beta-CD) to explore other early intermediates in more detail. We observed a transient LC-MS peak with a [M-H] at 192 Da that was tentatively identified as 4,6-dinitro-2,4,6-triaza-hexanal (O2NNHCH2NNO2CH2NHCHO, III) considered as the hydrolyzed product of II. In addition, we detected another novel intermediate with a [M-H] at 148 Da that was tentatively identified as a hydrolyzed product of III, namely, 5-hydroxy-4-nitro-2,4-diaza-pentanal (HOCH2NNO2CH2NHCHO, IV). Both III and IV can act as precursors to 4-NDAB. In the case of the polycyclic nitramine 2,4,6,8,10,12-hexanitro-2,4,6,8,10,12-hexaazaisowurtzitane (CL-20), denitration (two NO2-) also led to the formation of HCOOH, NH3, and N2O, but neither HCHO nor 4-NDAB were detected. The results provide strong evidence that initial denitration of cyclic nitramines in water is sufficient to cause ring cleavage followed by spontaneous decomposition to form the final products.

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Year:  2003        PMID: 12775055     DOI: 10.1021/es020959h

Source DB:  PubMed          Journal:  Environ Sci Technol        ISSN: 0013-936X            Impact factor:   9.028


  9 in total

1.  Iron-Dependent Enzyme Catalyzes the Initial Step in Biodegradation of N-Nitroglycine by Variovorax sp. Strain JS1663.

Authors:  Kristina M Mahan; Hangping Zheng; Tekle T Fida; Ronald J Parry; David E Graham; Jim C Spain
Journal:  Appl Environ Microbiol       Date:  2017-07-17       Impact factor: 4.792

2.  Biodegradation of cyclic nitramines by tropical marine sediment bacteria.

Authors:  Manish Bhatt; Jian-Shen Zhao; Fanny Monteil-Rivera; Jalal Hawari
Journal:  J Ind Microbiol Biotechnol       Date:  2005-05-25       Impact factor: 3.346

3.  Reduction of a Heme Cofactor Initiates N-Nitroglycine Degradation by NnlA.

Authors:  Kara A Strickland; Ashley A Holland; Alan Trudeau; Ilana Szlamkowicz; Melanie J Beazley; Vasileios A Anagnostopoulos; David E Graham; Jonathan D Caranto
Journal:  Appl Environ Microbiol       Date:  2022-08-02       Impact factor: 5.005

4.  Initial reaction(s) in biotransformation of CL-20 is catalyzed by salicylate 1-monooxygenase from Pseudomonas sp. strain ATCC 29352.

Authors:  Bharat Bhushan; Annamaria Halasz; Jim C Spain; Jalal Hawari
Journal:  Appl Environ Microbiol       Date:  2004-07       Impact factor: 4.792

5.  Experimental Design for One Dimensional Electrolytic Reactive Barrier for Remediation of Munition Constituent in Groundwater.

Authors:  David B Gent; Altaf Wani; Akram N Alshawabkeh
Journal:  Electrochim Acta       Date:  2012-04-19       Impact factor: 6.901

6.  Biodegradation of the hexahydro-1,3,5-trinitro-1,3,5-triazine ring cleavage product 4-nitro-2,4-diazabutanal by Phanerochaete chrysosporium.

Authors:  Diane Fournier; Annamaria Halasz; Jim Spain; Ronald J Spanggord; Jeffrey C Bottaro; Jalal Hawari
Journal:  Appl Environ Microbiol       Date:  2004-02       Impact factor: 4.792

7.  Aerobic biodegradation of HMX by Planomicrobium flavidum.

Authors:  Shilpi Nagar; Ajay Kumar Shaw; Shalini Anand; S Mary Celin; Pramod Kumar Rai
Journal:  3 Biotech       Date:  2018-10-19       Impact factor: 2.406

8.  Exploring the Distinct Distribution of Archaeal Communities in Sites Contaminated with Explosives.

Authors:  Yash Pal; Shanmugam Mayilraj; Srinivasan Krishnamurthi
Journal:  Biomolecules       Date:  2022-03-23

9.  Biodegradation of the high explosive hexanitrohexaazaiso-wurtzitane (CL-20).

Authors:  Pelin Karakaya; Christos Christodoulatos; Agamemnon Koutsospyros; Wendy Balas; Steve Nicolich; Mohammed Sidhoum
Journal:  Int J Environ Res Public Health       Date:  2009-04-09       Impact factor: 3.390

  9 in total

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