Fungal transformation of 2,4-dinitrotoluene and 2,4,6-trinitrotoluene.

Screening of 190 fungi representing 98 genera showed that the ability to transform 2,4,6-trinitrotoluene was common, whereas transformation of 2,4-dinitrotoluene was rare.     

Microbial transformation of 2,4,6-trinitrotoluene

The manufacture and decommissioning of explosives has generated, and continues to generate, large quantities of waste material whose primary toxic and mutagenic component is 2,4,6-trinitrotoluene (TNT). The magnitude of this problem has motivated a great deal of research into treatment processes and environmental fate studies, including characterization of microbial transformations of TNT. This work has encompassed studies with mixed cultures and pure cultures of microorganisms derived from either TNT-exposed or unexposed sources, and studies using microorganisms chosen for their known capacities to degrade other pollutants. Several of these studies are discussed with regard to whether they identified a process that may lead to the complete detoxification or mineralization of TNT. Since oxygen can have a significant influence on the types of biochemical reactions that can occur and on the oxidation of intermediates of TNT transformation processes, studies in which oxygen was not excluded are discussed separately from studies conducted under anaerobic conditions. Received 31 October 1995/ Accepted in revised form 29 March 1996     

Microbial transformation of 2,4,6-trinitrotoluene and other nitroaromatic compounds.

A variety of nitroaromatic compounds, including 2,4,6-trinitrotoluene (TNT), were reduced by hydrogen in the presence of enzyme preparations from Veillonella alkalescens. Consistent with the proposed reduction pathway, R-NO2 H2 leads to R-NO H2 leads to R-NHOH H2 leads to R-NH2, 3 mol of H2 was utilized per mol of nitro group. The rates of reduction of 40 mono-, di-, and trinitroaromatic compounds by V. alkalescens extract were determined. The reactivity of the nitro groups depended on other substituents and on the position of the nitro groups relative to these substituents. In the case of the nitrotoluenes, the para-nitro group was the most readily reduced, the 4-nitro position of 2,4-dinitrotulene being reduced first. The pattern of reduction of TNT (disappearance of TNT and reduction products formed) depended on the type of preparation (cell-free extract, resting cells, or growing culture), on the species, and on the atmosphere (air or H2). The "nitro-reductase" activity of V. alkalescens extracts was associated with protein fractions, one having some ferredoxin-like properties and the other possessing hydrogenase activity. Efforts to eliminate hydrogenase from the reaction have thus far been unsuccessful. The question of whether ferredoxin acts as a nonspecific reductase for nitroaromatic compounds remains unresolved.     

Microbial transformation of 14C-labeled 2,4,6-trinitrotoluene in an activated-sludge system.

The fate of 14C-labeled 2,4,6-trinitrotoluene (TNT) in an activated-sludge system was investigated. No [14C]TNT could be detected in the contents of an aerated reactor after 3 to 5 days of incubation. No significant 14CO2 was formed, and the radioactivity was about equally divided between the floc and the supernatant. The radioactive carbon present in the microflora was mainly associated with the lipid and protein components, but the characteristic constituents of these compounds (e.g., fatty acids and amino acids) were not radioactive. The major part of the 14C present in the lipid and protein fractions was found in precipitates that formed in both fractions. The solubility properties and infrared spectra of these precipitates suggested that they are macromolecular structures of the polyamide type formed by the reaction of TNT biotransformation products with lipids, fatty acids, and protein constituents of the microbial flora. This hypothesis is further supported by the correspondence of the infrared spectrum of the lipid precipitate with that of a model compound synthesized from TNT transformation products and lipid precursors. The resistance of these macromolecules to further biodegradation was paralleled by the reported resistance to microbial attack of polyamides containing similar linkages.     

Microbial production of (2R, 4R)-2,4-pentanediol by enatioselective reduction of acetylacetone and stereoinversion of 2,4-pentanediol

Summary (2R, 4R)-2,4-Pentanediol was obtained by the enatioselective reduction of acetylacetone (2,4-pentanedione) with the resting cells of methanol yeast,Candida boidinii KK912 (IFO 10574). (2R, 4R)-2,4-Pentanediol was also obtained by the stereoinversion of the isomeric mixture of 2,4-pentanediol.     

Microbial Transformation of 2,4,6-Trinitrotoluene in Aerobic Soil Columns

2,4,6-Trinitrotoluene (TNT)-contaminated soil material of a former TNT production plant was percolated aerobically in soil columns. Nineteen days of percolation with a potassium phosphate buffer supplemented with glucose or glucose plus ammonium sulfate caused an over 90% decline in the amount of extractable nitroaromatics in soils containing 70 to 2,100 mg of TNT per kg (dry weight). In the percolation solution, a complete elimination of TNT was achieved. Mutagenicity and soil toxicity were significantly reduced by the percolation process. 4-N-Acetylamino-2-amino-6-nitrotoluene was generated in soil and percolation fluid as a labile TNT metabolite.     

Microbial decomposition of coumarin in soil

Microbial decomposition of coumarin was studied in samples of chernozem soil by manometric measurement of oxygen consumption, paper chromatography of aromatic metabolic intermediates in soil extract and measurement of their UV spectra, and by the technique of simultaneous adaptation. Coumarin is decomposed in soil viao-coumaric and melilotic acids and at least one other compound of aromatic character. The metabolic pathway including salicylic acid and catechol was not proved. A total of 39 strains of coumarin-decomposing bacteria were isolated from the soil, out of which 25 belong to the genusPseudomonas, 7 to the genusCellulomonas and 7 to the genusAchromobacter. A comparison of the counts of bacteria utilizing coumarin as a sole carbon source in garden soil, in two chernozem soil samples and in acidic brown soil showed that their occurrence bears no relation to the so-called total number of bacteria (grown on agar medium with yeast and soil extracts and with tryptone) or to the content of carbon and nitrogen in the soil, or to its acidity.     

Microbial decomposition of post-harvest sugarcane residue

A laboratory in situ composting study was conducted as a possible alternative method for the current practice of open air burning of post-harvest sugarcane residue by sugarcane farmers. In situ composting of the sugarcane residue by the indigenous bacteria and fungi was accelerated using molasses as an initial substrate. A one-time application of molasses boosted the soil microbial population. which started to decompose the ligno-cellulosic fractions of the residue. The study showed significant differences in several parameters among the control and molasses applied treatments, namely, visual decomposition of residue, bacterial and fungal population, soil pH, cellulose content, cellulase activity. and soil organic matter. Further study is needed to refine the process for the future application of this technology as a possible alternative to the current practice of open air burning of sugarcane residue by farmers.     

Synthetic studies in the series of polyene macrolide antibiotics. 5. Synthesis of methyl-2,4,6-trideoxy-2,4-di-C-methyl-alpha-L- gluco-hexopyranoside and methyl-2,4,6-trideoxy-2,4-di-C-methyl- alpha-L-manno-hexopyranoside, the stereoisomers of the C33-C38 fragment of amphotericin B

The synthesis of the gluco- and manno-stereoisomers of amphotericin B is described.     

Stability of hydroxylamino- and amino-intermediates from reduction of 2,4,6-trinitrotoluene, 2,4-dinitrotoluene, and 2,6-dinitrotoluene

Hydroxylamines, produced as intermediates in the reductive metabolism of 2,4,6-trinitrotoluene, 2,4-dinitrotoluene, and 2,6-dinitrotoluene between nitroaromatic parent compounds and corresponding amines, were unstable in aqueous solution in the presence of O₂. Reactions of hydroxylamines to compounds other than amines may be the major cause of poor mass balance observations in bioremediation systems where only aminated products are monitored. Results demonstrate the formation of azoxy compounds as products of abiotic aryl-hydroxylamine reactions.     

Synthesis of 2,4-diacetamido-2,4,6-trideoxy-L-altrose, -L-idose, and -L-talose from benzyl 6-deoxy-3,4-O-isopropylidene-beta-L-galactopyranoside

Acetylation of benzyl 6-deoxy-3,4O-isopropylidene-β-L-galactopyranoside gave benzyl 2-O-acetyl-6-deoxy-3,4-O-isopropylidene-β-L-galactopyranoside (1). Removal of the isopropylidene group afforded benzyl 2-O-acetyl-6-deoxy-β-L-galactopyranoside (2), which was converted into benzyl 2-O-acetyl-6-deoxy-3,4-di-O-(methyl-sulfonyl)-β-L-galactopyranoside (3). Benzyl 2,3-anhydro-6-deoxy-4-O-(methyl-sulfonyl)-β-L-gulopyranoside (4) was obtained from 3 by treatment with alkali. Reaction of 4 with sodium azide in N,N-dimethylformamide gave a mixture of two isomeric benzyl 2,4-diazido-2,4,6-trideoxy hexoses, the syrupy diazido derivative 5 and the crystalline benzyl 2,4-diazido-2,4,6-trideoxy-β-L-idopyranoside (6). Acetylation of 6 afforded a compound whose n.m.r. spectrum was completely first order and in agreement with the structure of benzyl 3-O-acetyl-2,4-diazido-2,4,6-trideoxy-β-L-idopyranoside (7). Lithium aluminium hydride reduction of 5, followed by acetylation, afforded a crystalline product (8), shown by n.m.r. spectroscopy to be benzyl 2,4-diacetamido-3-O-acetyl-2,4,6-trideoxy-β-L-altropyranoside. Similar treatment of the diazido derivative 6 afforded benzyl 2,4-diacetamido-3-O-acetyl-2,4,6-trideoxy-β-L-idopyranoside (9). Compounds 8 and 9 could also be obtained from 4 by treatment of the crude diazido mixture with lithium aluminium hydride, with subsequent N-acetylation. The syrupy benzyl 2,4-diacetamido-2,4,6-trideoxy-β-L-altropyranoside (10) and the crystalline benzyl 2,4-diacetamido-2,4,6-trideoxy-β-L-idopyranoside (11) thus obtained were then O-acetylated to give 8 and 9 respectively. Benzyl 2,4-diacetamido-2,4,6-trideoxy-β-L-talopyranoside (15) was obtained from 11 by treatment with methanesulfonyl chloride and subsequent solvolysis. Compound 15 was O-acetylated to yield benzyl 2,4-diacetamido-3-O-acetyl-2,4,6-trideoxy-β-L-talopyranoside (16). the n.m.r. spectrum of which was in full agreement with the assigned structure. The mass spectra of compounds 8–11, 15, and 16 were also in agreement with their proposed structures. Removal of the benzyl groups from 10, 11 and 15 afforded the corresponding 2,4-diacetamido-2,4,6-trideoxyhexoses 12, 13, and 17, having the L-altro, L-ido, and L-talo configurations, respectively.     

Bioremediation 2,4,6,-Trichlorophenol (2,4,6-TCP) by Shigella sp. S2 Isolated from Industrial Dumpsite

A bacterium that utilizes 2,4,6-trichlorophenol (2,4,6-TCP) as a sole source of carbon and energy was isolated from an industrial dumpsite, the bacterium designated as strain S2. Degradation was routinely monitored by observing growth analysis, chloride release assay, and ring cleavage activity and was further confirmed by gas chromatography (GC) analysis. The bacterium was found to degrade up to 90% of 2,4,6-TCP at 1.5 mM concentration. The bacteria were characterized morphologically, biochemically, and by 16S rRNA gene sequencing, which showed 99% sequence similarity with Shigella sp. This is the first report that Shigella sp. was able to degrade 2,4,6-TCP. This strain was found to be novel and a potential 2,4,6-TCP degrader. Further, this strain may be used for bioremediation of 2,4,6-TCP–containing waste in the environment.     

Microbial decomposition of 3,4-dichloroaniline, adsorbed by activated charcoal]

The accessibility of 3,4-dichloroaniline (DCA) sorbed by activated carbon to degradative microorganisms was studied. A Paracoccus denitrificans strain capable of growing on medium with DCA as the only source of energy, carbon, and nitrogen was used in the experiment. The high sorption capacity of all the carbons studied (powdered RS and SKT-6A and granular AG-3) in relation to DCA (350 to 360, 480 to 520, and 540 to 580 mg/g, respectively) was demonstrated. The sorption capacity correlated positively with the specific surface area and the total volume of the sorbent micropores. The bulk of the DCA was reversibly sorbed and amenable to microbial decomposition; however, the decomposition rates significantly differed. When RS, SKT, and Agrosorb preliminarily saturated with DCA were incubated in a culture of P. denitrificans, the bulk of the reversibly sorbed DCA was decomposed (in the absence of the other carbon sources) in 2, 5, and 10 weeks, respectively, after which the process slowed down. At the end of the experiment (29 weeks), 81 to 87% of the DCA underwent full mineralization, which was accompanied by the release of chlorine ions; a small fraction of the xenobiotic (0.8 to 1.9%) remained a reversibly sorbed fraction (extractable with acetone), and 12 to 17% of the initial DCA seemed to have been chemically transformed and bound by carbon. The studied carbons may be used in biological decontamination of chloroaniline-polluted soils to decrease the toxic effect of chloroanilines on microorganisms.     

Reaction of 1-fluoro-2,4-dinitrobenzene and 2,4,6-trinitrobenzenesulphonic acid with membranes of sarcoplasmic reticulum.

Membranes of sarcoplasmic reticulum were labelled with 1-fluoro-2,4-dinitro[3H]benzene at pH 6.5 and with 2,4,6-trinitrobenzenesulphonate at pH 9.2. Conditions were chosen to restrict reaction to amino groups, and the effect of blockings of these groups by methyl acetimidate was determined. All proteins were labelled to some extent by both reagents, but, whereas the trinitrophenylation of both lipid and protein amino groups was almost completely blocked by methyl acetimidate, the dinitrophenylation of the ATPase at pH 6.5 was much less affected. The seven amino groups on the ATPase that were labelled under these conditions did not react with methyl acetimidate. This reagent can therefore be used to enhance the specificity of fluorodinitrobenzene for amino groups in a hydrophobic environment. The amino groups on the minor proteins and on the phospholipids that reacted with fluorodinitrobenzene at pH 6.5 were probably in an aqueous environment, since the reaction was blocked by methyl acetimidate.     

Initial Reductive Reactions in Aerobic Microbial Metabolism of 2,4,6-Trinitrotoluene

Because of its high electron deficiency, initial microbial transformations of 2,4,6-trinitrotoluene (TNT) are characterized by reductive rather than oxidation reactions. The reduction of the nitro groups seems to be the dominating mechanism, whereas hydrogenation of the aromatic ring, as described for picric acid, appears to be of minor importance. Thus, two bacterial strains enriched with TNT as a sole source of nitrogen under aerobic conditions, a gram-negative strain called TNT-8 and a gram-positive strain called TNT-32, carried out nitro-group reduction. In contrast, both a picric acid-utilizing Rhodococcus erythropolis strain, HL PM-1, and a 4-nitrotoluene-utilizing Mycobacterium sp. strain, HL 4-NT-1, possessed reductive enzyme systems, which catalyze ring hydrogenation, i.e., the addition of a hydride ion to the aromatic ring of TNT. The hydride-Meisenheimer complex thus formed (H⁻-TNT) was further converted to a yellow metabolite, which by electrospray mass and nuclear magnetic resonance spectral analyses was established as the protonated dihydride-Meisenheimer complex of TNT (2H⁻-TNT). Formation of hydride complexes could not be identified with the TNT-enriched strains TNT-8 and TNT-32, or with Pseudomonas sp. clone A (2NT⁻), for which such a mechanism has been proposed. Correspondingly, reductive denitration of TNT did not occur.     

Synthetic studies in the series of polyene macrolide antibiotics. 4. Synthesis of methyl-2,4,6-trideoxy-3-0-benzoyl-2,4-di-C-methyl- alpha-L-talo-hexopyranoside and 2,4,6-trideoxy-2,4-di-C-methyl-L- galactitol, the stereoisomers of the fragment C33-C38 of amphotericin B

Synthesis of methyl 2,4,6-trideoxy-3-O-benzoyl-2,4-di-C-methyl-alpha-L-talohexopyranoside and 2,4,6-trideoxy-2,4-di-C-methyl-L-galactitol, stereoisomers of the C33-C38 fragment of amphothericin B, is described.