Biotransformation Patterns of 2,4,6-Trinitrotoluene by Aerobic Bacteria

2,4,6-Trinitrotoluene (TNT), a toxic nitroaromatic explosive, accumulates in the environment, making necessary the remediation of contaminated areas and unused materials. Although bioremediation has been utilized to detoxify TNT, the metabolic processes involved in the metabolism of TNT have proven to be complex. The three aerobic bacterial strains reported here (Pseudomonas aeruginosa, Bacillus sp., and Staphylococcus sp.) differ in their ability to biotransform TNT and in their growth characteristics in the presence of TNT. In addition, enzymatic activities have been identified that differ in the reduction of nitro groups, cofactor preferences, and the ability to eliminate-NO₂ from the ring. The Bacillus sp. has the most diverse bioremediation potential owing to its growth in the presence of TNT, high level of reductive ability, and capability of removing-NO₂ from the nitroaromatic ring. Received: 16 May 1997 / Accepted: 19 July 1997     

Biotransformation of 2,4,6-Trinitrotoluene by Pure Culture Ruminal Bacteria

Twenty-one ruminal bacteria species were tested for their ability to degrade 2,4,6-trinitrotoluene (TNT) within 24 h. Butyrivibrio fibrisolvens, Fibrobacter succinogenes, Lactobacillus vitulinus, Selenomonas ruminantium, Streptococcus caprinus, and Succinivibrio dextrinosolvens were able to completely degrade 100 mg/L TNT, with <5% of the original TNT recovered as diaminonitrotoluene metabolites. Eubacterium ruminantium, Lactobacillus ruminis, Ruminobacter amylophilus, Streptococcus bovis, and Wolinella succinogenes were able to completely degrade 100 mg/L TNT, with 23–60% of the TNT recovered as aminodinitrotoluene and/or diaminonitrotoluene metabolites. Clostridium polysaccharolyticum, Megasphaera elsdenii, Prevotella bryantii, Prevotella ruminicola, Ruminococcus albus, and Ruminococcus flavefaciens were able to degrade 80–90% of 100 mg/L TNT. Desulfovibrio desulfuricans subsp. desulfuricans, Prevotella albensis, and Treponema bryantii degraded 50–80% of the TNT. Anaerovibrio lipolytica was completely inhibited by 100 mg/L TNT. These results indicate that a variety of rumen bacteria is capable of transforming TNT.     

Anaerobic/Aerobic Composting of Soil Contaminated with 2,4,6-Trinitrotoluene

A loam soil from Pennsylvania without a history of exposure to explosives was incubated with 5 g kg^-1 of ¹⁵N-labeled 2,4,6-trinitrotoluene (TNT) and 200 μCi kg^-1 of ¹⁴C-TNT for 3 days and then amended with compost at a 1:2 soil to compost ratio. The compost was prepared by mixing 40% alfalfa hay, 40% grass hay, 10% spent mushroom compost, and 10% municipal biosolids. The mixture of soil and compost was inoculated with methanogens from cattle manure, amended with glucose and starch, and incubated for 37 days under anaerobic conditions. The anaerobic incubation was followed by 26 days of forced aerobic incubation. At the end of the aerobic phase, most of the radioactivity was associated with organic matter; only 8.7% could be extracted with water and methanol, but no TNT was present in the extracts as determined by high-performance liquid chromatography. The unextractable radioactivity was associated with humic acid (40.0±1.0%), fulvic acid (14.3±1.4%), and humin (28.2±0.5%). Radioactive materials associated with humic acid and humin were analyzed by solid-state ¹⁵N-nuclear magnetic resonance (NMR) spectrometry. The NMR spectra indicated that nitro groups of TNT had been reduced to amino groups thatwere subsequently involved in the formation of covalent bonds with soil organic matter.     

Biotransformation of 2,4,6-Trinitrotoluene with Phanerochaete chrysosporium in Agitated Cultures at pH 4.5

The biotransformation of 2,4,6-trinitrotoluene (TNT) (175 μM) by Phanerochaete chrysosporium with molasses and citric acid at pH 4.5 was studied. In less than 2 weeks, TNT disappeared completely, but mineralization (liberated ¹⁴CO₂) did not exceed 1%. A time study revealed the presence of several intermediates, marked by the initial formation of two monohydroxylaminodinitrotoluenes (2- and 4-HADNT) followed by their successive transformation to several other products, including monoaminodinitrotoluenes (ADNT). A group of nine acylated intermediates were also detected. They included 2-N-acetylamido-4,6-dinitrotoluene and its p isomer, 2-formylamido-4,6-dinitrotoluene and its p isomer (as acylated ADNT), 4-N-acetylamino-2-amino-6-nitrotoluene and 4-N-formylamido-2-amino-6-nitrotoluene (as acetylated DANT), 4-N-acetylhydroxy-2,6-dinitrotoluene and 4-N-acetoxy-2,6-dinitrotoluene (as acetylated HADNT), and finally 4-N-acetylamido-2-hydroxylamino-6-nitrotoluene. Furthermore, a fraction of HADNTs were found to rearrange to their corresponding phenolamines (Bamberger rearrangement), while another group dimerized to azoxytoluenes which in turn transformed to azo compounds and eventually to the corresponding hydrazo derivatives. After 30 days, all of these metabolites, except traces of 4-ADNT and the hydrazo derivatives, disappeared, but mineralization did not exceed 10% even after the incubation period was increased to 120 days. The biotransformation of TNT was accompanied by the appearance of manganese peroxidase (MnP) and lignin-dependent peroxidase (LiP) activities. MnP activity was observed almost immediately after TNT disappearance, which was the period marked by the appearance of the initial metabolites (HADNT and ADNT), whereas the LiP activity was observed after 8 days of incubation, corresponding to the appearance of the acyl derivatives. Both MnP and LiP activities reached their maximum levels (100 and 10 U/liter, respectively) within 10 to 15 days after inoculation.     

Products of Anaerobic 2,4,6-Trinitrotoluene (TNT) Transformation by Clostridium bifermentans

Experiments to elucidate the 2,4,6-trinitrotoluene (TNT)-transforming activity of Clostridium bifermentans LJP-1 identified reductive TNT transformations that ultimately produced as end products triaminotoluene (TAT) and phenolic products of TAT hydrolysis. An adduct of TAT, apparently formed by condensation of TAT and pyruvic aldehyde (methyl glyoxal), was also detected.     

The Role of Oxophytodienoate Reductases in the Detoxification of the Explosive 2,4,6-Trinitrotoluene by Arabidopsis

The explosive 2,4,6-trinitrotoluene (TNT) is a significant environmental pollutant that is both toxic and recalcitrant to degradation. Phytoremediation is being increasingly proposed as a viable alternative to conventional remediation technologies to clean up explosives-contaminated sites. Despite the potential of this technology, relatively little is known about the innate enzymology of TNT detoxification in plants. To further elucidate this, we used microarray analysis to identify Arabidopsis (Arabidopsis thaliana) genes up-regulated by exposure to TNT and found that the expression of oxophytodienoate reductases (OPRs) increased in response to TNT. The OPRs share similarity with the Old Yellow Enzyme family, bacterial members of which have been shown to transform explosives. The three predominantly expressed forms, OPR1, OPR2, and OPR3, were recombinantly expressed and affinity purified. Subsequent biochemical characterization revealed that all three OPRs are able to transform TNT to yield nitro-reduced TNT derivatives, with OPR1 additionally producing the aromatic ring-reduced products hydride and dihydride Meisenheimer complexes. Arabidopsis plants overexpressing OPR1 removed TNT more quickly from liquid culture, produced increased levels of transformation products, and maintained higher fresh weight biomasses than wild-type plants. In contrast, OPR1,2 RNA interference lines removed less TNT, produced fewer transformation products, and had lower biomasses. When grown on solid medium, two of the three OPR1 lines and all of the OPR2-overexpressing lines exhibited significantly enhanced tolerance to TNT. These data suggest that, in concert with other detoxification mechanisms, OPRs play a physiological role in xenobiotic detoxification.Large amounts of land and water are heavily contaminated by explosives, mainly as a result of the manufacture and military use of munitions. The high financial cost associated with cleaning up these contaminated sites largely precludes the use of many existing remediation technologies, such as soil excavation and incineration or disposal to landfill. There is a great deal of work documenting the global contamination, general toxicity, and microbial metabolism of 2,4,6-trinitrotoluene (TNT) in the environment; however, relatively little is known about the enzymes mediating the detoxification of TNT in plants (for review, see Rylott and Bruce, 2009).Phytoremediation, the use of plants to remove environmental pollutants, offers a low-cost, sustainable alternative to conventional remediation technologies and is attracting considerable attention as a means to clean up sites contaminated with explosives. While TNT is a potent phytotoxin, plants are able to detoxify low levels of TNT. In an effort to determine how plant tolerance could be further improved, we are investigating the biochemistry and enzymology underlying the innate ability of plants to detoxify TNT. The detoxification of xenobiotics has been loosely categorized into three phases (Sandermann, 1992): activation, conjugation, and compartmentation. The proposed route of TNT detoxification follows these phases. The electron-withdrawing properties of the nitro groups of TNT make the aromatic ring electron deficient. This favors reductive transformation reactions in plants, and the TNT molecule is most commonly activated by the reduction of a nitro group to give hydroxylamino and then amino derivatives (Fig. 1, pathway A). Following the introduction of a functional group, more hydrophilic molecules such as Glc are conjugated to the activated TNT molecule (Gandia-Herrero et al., 2008), facilitating transport and subsequent compartmentation or sequestration.Open in a separate windowFigure 1.The transformation of TNT by pentaerythritol tetranitrate reductase. Pathway A shows the transformation of the nitro group to nitroso-dinitrotoluene (NODNT), HADNT, and then ADNT products. Pathway B shows the reduction of the aromatic ring to form hydride and dihydride Meisenheimer complexes, then chemical condensation with HADNT to form diarylamines.Data from both our microarray experiments (Gandia-Herrero et al., 2008) and other expression studies (Ekman et al., 2003; Mezzari et al., 2005) have found that members of the small gene family of oxophytodienoate reductases (OPRs) in Arabidopsis (Arabidopsis thaliana) are up-regulated following exposure to TNT. The Arabidopsis genome contains three characterized OPRs: OPR1, OPR2, and OPR3. In addition, there are three as yet uncharacterized putative OPRs, named here as OPR4, OPR5, and OPR6, with OPR4 and OPR5 being identical. The physiological functions of the OPRs remain obscure, with the exception of OPR3, which is involved in jasmonic acid biosynthesis, converting (9S,13S)-12-oxophytodienoic acid to 3-2(2′(Z)-pentyl)cyclopentane-1-octanoic acid in the peroxisome (Sanders et al., 2000; Stintzi and Browse, 2000; for review, see Wasternack, 2007). OPR3 is located on chromosome II within the Arabidopsis genome and contains a C-terminal Ser-Arg-Leu type 1 peroxisome-targeting sequence. The remaining OPRs are all located on chromosome I and do not possess any known organelle-targeting sequences. The spatial expression of OPR1 and OPR2 across root cells where TNT accumulates (Biesgen and Weiler, 1999; Baerenfaller et al., 2008) favors a role in detoxification.The OPRs share similarity with the Old Yellow Enzyme family, a group of flavoenzymes that has been repeatedly associated with the transformation of explosives (Binks et al., 1996; Schaller and Weiler, 1997; Snape et al., 1997; Basran et al., 1998; French et al., 1998; Blehert et al., 1999; Pak et al., 2000; Fitzpatrick et al., 2003; Williams et al., 2004). Studies also indicate that Old Yellow Enzyme homologs function as antioxidants, detoxifying the breakdown products of lipid peroxidation and other toxic electrophilic compounds (Kohli and Massey, 1998; Williams and Bruce, 2002; Fitzpatrick et al., 2003; Trotter et al., 2006). This oxidative stress could result from exposure to xenobiotics including TNT, wounding, or pathogen attack.Pentaerythritol tetranitrate reductase, an Old Yellow Enzyme homolog isolated from Enterobacter cloacae (Binks et al., 1996), possesses two catalytic activities toward TNT (Fig. 1): nitroreduction of TNT to form hydroxylamino-dinitrotoluene (HADNT) and then amino-dinitrotoluene (ADNT), and aromatic ring reduction of TNT to yield hydride and dihydride (2H⁻-TNT) Meisenheimer TNT adducts (French et al., 1998; Williams et al., 2004). The TNT ring-reduced compounds condense via a nonenzymatic reaction with HADNTs to form diarylamines, with the liberation of nitrite (Wittich et al., 2008). Expression of pentaerythritol tetranitrate reductase in tobacco (Nicotiana tabacum) confers both resistance to, and the ability to transform, TNT (French et al., 1999). OPR1, OPR2, and OPR3 share 43%, 44%, and 36% identity, respectively, with pentaerythritol tetranitrate reductase, and all possess the conserved active site amino acids crucial for TNT transformation by pentaerythritol tetranitrate reductase and other members of the Old Yellow Enzyme family (Snape et al., 1997; French et al., 1998; Khan et al., 2004), suggesting that they are capable of transforming TNT.The OPR4/5 protein is predicted to have reduced activity toward TNT, compared with the other OPRs, owing to a C-terminal truncation that removes residues thought to be important in binding the cofactor NADH, Thus, we investigated OPR1, -2, and -3 as likely candidates for the TNT nitroreduction activity in Arabidopsis.     

Characterization of Metabolites during Biodegradation of Hexahydro-1,3,5-Trinitro-1,3,5-Triazine (RDX) with Municipal Anaerobic Sludge

The biodegradation of hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX) in liquid cultures with municipal anaerobic sludge showed that at least two degradation routes were involved in the disappearance of the cyclic nitramine. In one route, RDX was reduced to give the familiar nitroso derivatives hexahydro-1-nitroso-3,5-dinitro-1,3,5-triazine (MNX) and hexahydro-1,3-dinitroso-5-nitro-1,3,5-triazine (DNX). In the second route, two novel metabolites, methylenedinitramine [(O₂NNH)₂CH₂] and bis(hydroxymethyl)nitramine [(HOCH₂)₂NNO₂], formed and were presumed to be ring cleavage products produced by enzymatic hydrolysis of the inner C—N bonds of RDX. None of the above metabolites accumulated in the system, and they disappeared to produce nitrous oxide (N₂O) as a nitrogen-containing end product and formaldehyde (HCHO), methanol (MeOH), and formic acid (HCOOH) that in turn disappeared to produce CH₄ and CO₂ as carbon-containing end products.     

三硝基甲苯致白内障机理及其在晶状体内代谢的研究

在建立TNT大鼠白内障的基础上,用HPLC分析了晶状体内TNT及其代谢产物,并用ESR及NBT方法检测了TNT在晶状体内的代谢过程所产生的自由基。结果表明,慢性染毒24个月的大鼠白内障晶状体内含有TNT原形和4氨基2,6二硝基甲苯代谢产物,以及在体外与正常晶状体微粒体孵育可产生TNT硝基阴离子自由基和超氧阴离子自由基。上述结果提示,TNT可进入晶状体内,在其还原代谢过程中产生硝基阴离子自由基中间产物,在有氧条件下进而产生超氧阴离子自由基,这可能是TNT导致白内障的启动因素。     

三硝基甲苯致晶状体上皮细胞DNA损伤作用的研究

本文通过出生后７天和２４个月两组大鼠晶状体与２０％三硝基甲苯（ＴＮＴ）甘油：水（８：２）混悬液体外培养,培养箱通５％ＣＯ２,恒温３７℃,观察ＴＮＴ对晶状体上皮细胞ＤＮＡ的损伤程度,结果以反映单链ＤＮＡ断裂强度的Ｆ６３０／Ｆ５３０比值表示。ＨＰＬＣ分析发现经体外ＴＮＴ孵育的晶状体内含有ＴＮＴ及其代谢产物;当共同培养９６ｈ后,Ｆ６４０／Ｆ５３０比值随着ＴＮＴ剂量增加而增大,达到４０μＬ（１１．７４μｍｏｌ／Ｌ）时趋向平稳;当用ＴＮＴ浓度为４．４０μｍｏｌ／Ｌ的相同剂量培养时,４８小时后单链ＤＮＡ断裂最为严重Ｆ６３０／Ｆ５３０比值为１．５０,明显高子正常对照组（Ｐ＜０．０１）;幼鼠单链ＤＮＡ断裂程度显著高于老龄鼠（Ｐ＜０．０１）。     

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.     

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.     

Accelerated Transformation and Binding of 2,4,6-Trinitrotoluene in Rhizosphere Soil

Enhanced microbial activity and xenobiotic transformations take place in the rhizosphere. Degradation and binding of 2,4,6-trinitrotoluene (TNT) were determined in two rhizosphere soils (RS) and compared to respective unplanted control soils (CS). The rhizosphere soils were obtained after growing corn for 70 d in soils containing 2.8% (Soil A) or 5.9% (Soil B) organic matter. Aerobically agitated soil slurries (3:1, solution/soil) were prepared from RS and CS and amended with 75 mg TNT L^-1 (¹⁴C-labeled). TNT degraded more rapidly and formed more un-extractable bound residue in RS than in CS. In Soil A, total extractable TNT decreased from 225 to 1.0 mg kg^-1 in RS, whereas 11 mg kg^-1 remained in CS after 15 d. Unextractable bound ¹⁴C residues accounted for 40% of the added ¹⁴C-TNT in RS and 28% in CS. The smaller differences in Soil B were attributed partially to the higher organic matter content. The predominant TNT degradation products were monoaminodinitrotoluenes (ADNT), which accumulated and disappeared more rapidly in RS than in CS, and hydroxylaminodinitrotoluenes (HADNT). When sterilized by γ-irradiation, no significant differences between RS and CS were observed in TNT loss or bound residue formation. More rapid TNT degradation and enhanced bound residue formation in the unsterilized RS was attributed to micro-bial-facilitated production and transformation of HADNT and ADNT, which are potential precursors to bound residue formation. If plants can be established on TNT-contaminated soil, these results indicate that the rhizosphere can accelerate reductive transformation of TNT and promote bound residue formation.     

Transformation of 2,4,6-Trinitrotoluene by Pseudomonas pseudoalcaligenes JS52

Pseudomonas pseudoalcaligenes JS52 grows on nitrobenzene via partial reduction of the nitro group and enzymatic rearrangement of the resultant hydroxylamine. Cells and cell extracts of nitrobenzene-grown JS52 catalyzed the transient formation of 4-hydroxylamino-2,6-dinitrotoluene (4HADNT), 4-amino-2,6-dinitrotoluene (4ADNT), and four previously unidentified metabolites from 2,4,6-trinitrotoluene (TNT). Two of the novel metabolites were identified by liquid chromatography/mass spectrometry and (sup1)H-nuclear magnetic resonance spectroscopy as 2,4-dihydroxylamino-6-nitrotoluene (DHANT) and 2-hydroxylamino-4-amino-6-nitrotoluene (2HA4ANT). A polar yellow metabolite also accumulated during transformation of TNT by cells and cell extracts. Under anaerobic conditions, extracts of strain JS52 did not catalyze the production of the yellow metabolite or release nitrite from TNT; moreover, DHANT and 2HA4ANT accumulated under anaerobic conditions, which indicated that their further metabolism was oxygen dependent. Small amounts of nitrite were released during transformation of TNT by strain JS52. Sustained transformation of TNT by cells required nitrobenzene, which indicated that TNT transformation does not provide energy. Transformation of TNT catalyzed by enzymes in cell extracts required NADPH. Transformation experiments with (sup14)C-TNT indicated that TNT was not mineralized; however, carbon derived from TNT became associated with cells. Nitrobenzene nitroreductase purified from strain JS52 transformed TNT to DHANT via 4HADNT, which indicated that the nitroreductase could catalyze the first two steps in the transformation of TNT. The unusual ability of the nitrobenzene nitroreductase to catalyze the stoichiometric reduction of aromatic nitro compounds to the corresponding hydroxylamine provides the basis for the novel pathway for metabolism of TNT.     

Alternative Pathways of the Initial Transformation of 2,4,6-Trinitrotoluene by Yeasts

A new model for the initial transformation of 2,4,6-trinitrotoluene (TNT) by facultatively anaerobic and aerobic yeasts is presented. The model is based on the data that Saccharomyces sp. ZS-A1 was able to reduce the nitrogroups of TNT with the formation of 2- and 4-hydroxyaminodinitrotoluenes (2-HADNT and 4-HADNT) as the major early TNT metabolites (the molar HADNT/TNT ratio reached 0.81), whereas aminodinitrotoluenes (ADNTs) and the hydride-Meisenheimer complex of TNT (H-TNT) were the minor products. Candidasp. AN-L13 almost completely transformed TNT into H-TNT through the reduction of the aromatic ring. Candida sp. AN-L14 transformed TNT through a combination of the two mechanisms described. Aeration stimulated the production of HADNT from TNT, whereas yeast incubation under stationary conditions promoted the formation of HADNT. The transformation of TNT into HADNT led to a tenfold increase in the acute toxicity of the TNT preparation with respect to Paramecium caudatum, whereas the increase in the toxicity was about twofold in the case of the alternative attack at the aromatic ring.     

Mass Balance Studies with 14C-Labeled 2,4,6-Trinitrotoluene (TNT) Mediated by an Anaerobic Desulfovibrio Species and an Aerobic Serratia Species

Investigations were carried out to evaluate the level of incorporation of radiolabeled 2,4,6-trinitrotoluene (TNT) and metabolites into the bacterial biomass of two different bacterial species after cometabolically mediated TNT transformation. Biotransformation experiments with ¹⁴C-TNT indicated that TNT was not mineralized; however, carbon derived from TNT became associated with the cells. It was found that more than 42% of the initially applied radiolabel was associated with the cell biomass after cometabolic ¹⁴C-TNT transformation with the strictly anerobic Desulfovibrio species strain SHV, whereas with the strictly aerobic Serratia plymuthica species strain B7, 32% of cell-associated ¹⁴C activity was measured. The remainder of the radiolabel was present in the supernatants of the liquid cultures in the form of different TNT metabolites. Under anoxic conditions with the Desulfovibrio species, TNT was ultimately transformed to 2,4,6-triaminotoluene (TAT) and both diaminonitrotoluene isomers, whereas under oxic conditions with the Serratia species, TNT was converted to hydroxylaminodinitrotoluenes and aminodinitrotoluenes, with 4-amino-2,6-dinitrotoluene (4ADNT) being the major end product. In both culture supernatants, small amounts of very polar, radiolabeled, but unidentified metabolites were detected. At the end of the experiments approximately 92% and 96% of the originally applied radioactivity was recovered in the studies with the Serratia and Desulfovibrio species, respectively. Received: 21 May 1998 / Accepted: 6 July 1998     

Specific Toxic Effects of 2,4,6-Trinitrotoluene on Bacillus subtilisSK1

Using Bacillus subtilis SK1 as an example, it was demonstrated for the first time that 2,4,6-trinitrotoluene (TNT) transformation pathways change with TNT concentration. The growth of cultured B. subtilis SK1, delayed at 20 mg/l TNT (minimum toxic concentration), was resumed following TNT transformation. Aromatic amines were predominant metabolites detected in the culture medium at early stages of TNT transformation. The culture growth was completely inhibited by 200 mg/l TNT. As this took place, nitrites accumulated in the culture medium.     

Fate and Transport of 2,4,6-Trinitrotoluene in Loams at a Former Explosives Factory

Natural attenuation processes affecting 2,4,6-trinitrotoluene (TNT) were determined within loams for two study areas at the former Explosives Factory Maribyrnong, Australia. TNT fate and transport was investigated through spectrophotometric/High Performance Liquid Chromatography (HPLC) analyses of soil and groundwater, adsorption and microcosm testwork. A five tonne crystalline TNT source zone delineated within near surface soils at the base of a TNT process waste lagoon was found to be supplying aqueous TNT loading (7 ppm) to subsurface soils and groundwater. The resultant plume was localized within the loam aquitard due to a combination of natural attenuation processes and hydrogeological constraints, including low hydraulic conductivity and upward hydraulic gradients. Freundlich described sorptive partitioning was the main TNT sink (K_F = 29 mL/g), while transformation rates were moderate (1.01 × 10^-4 h^-1) under the aerobic conditions. Increasing 2-amino-4,6-dinitrotoluene predominance over 4-amino-2,6-dinitrotoluene was discovered with depth (in situ) and time (microcosms). Simplified dissolution rate calculations indicate that without mitigation of the TNT source, contaminant persistence within the vadose zone may approach 2000 years, while ATRANS20 simulations demonstrate that the TNT plume propagates very slowly along the flow path within the aquitard.     

Derivation of Environmental Soil Quality Guidelines for 2,4,6-Trinitrotoluene Using the CCME Approach

The Protocol for the Derivation of Environmental and Human Health Soil Quality Guidelines of the Canadian Council of Ministers of the Environment was used to prepare preliminary Environmental Soil Quality Guidelines (SQG_E) for 2,4,6-trinitrotoluene (TNT). A thorough literature search led to the compilation of the existing toxicological data. Calculated Environmental Soil Quality Guidelines for TNT are SQG_E=0.02?mg/kg (preliminary value) for agricultural land use and 86?mg/kg for residential/park, commercial/industrial land use. Because of the lack of sufficient scientific information on the effects of TNT in soil on microbial processes, this type of evaluation was not possible. For oral toxicological data, laboratory animals were used instead of grazing and foraging species to determine the ingestion guideline since no related literature was found. Furthermore, this work has led to the identification of avenues of future research necessary to complete the task at hand. The research should focus on specific studies involving direct contact between the organisms and the soil, in order to: (1) develop a database of effects of TNT on microbial processes, (2) study the effects of TNT ingestion on birds and grazing herbivores, (3) determine plant bioconcentration factors, and (4) observe in situ the toxic effects after direct contact exposure.     

Comparison of 2,4,6-Trinitrotoluene Degradation by Seven Strains of White Rot Fungi

The degradation of 2,4,6-trinitrotoluene (TNT) by seven strains of white rot fungi was examined in two different media containing 50 mg L⁻¹ of TNT. When TNT was added into a nutrient-rich YMG medium at the beginning of the incubation, four of the fungal strains completely removed TNT during several days of incubation and showed higher removal rates than those of Phanerochaete chrysosporium. TNT added into YMG medium after a 5-day preincubation period completely disappeared within 12 hours, and the removal rates were higher than those in N-limited minimal medium. Isomers of hydroxylamino-dinitrotoluene were identified as the first detectable metabolites of TNT. These were transformed to amino-dinitrotoluenes, which also disappeared during further incubation from cultures of Irpex lacteus. During the initial phase of TNT degradation by I. lacteus, dinitrotoluenes were also detected after the transient formation of a hydride-Meisenheimer complex, indicating that I. lacteus used two different pathways of TNT degradation simultaneously. Received: 29 March 2000 / Accepted: 23 May 2000     

Biotransformation of 1-Nitropyrene in Intestinal Anaerobic Bacteria

Mutagenic nitroaromatic compounds have recently been found in photocopies, urban atmosphere, automobile exhaust and wastewater. 1-Nitropyrene (1-NP) is readily formed when pyrene, ubiquitous in the environment, is exposed to nitrogen dioxide in the urban atmosphere or in automobile exhaust, and is highly mutagenic, inducing 449 his⁺ revertants/plate/nmol from Salmonella typhimurium strain TA98 in the absence of S9 fraction in the Salmonella-microsome test. It is possible to swallow sputum or some food containing 1-NP and it would come into contact with the normal bacterial flora. We determined the 1-NP nitroreductase activity in environmental and laboratory bacterial strains. We found that the mutagenicity of 1-NP mixed with the feces of a healthy man or a culture of anaerobic bacteria was decreased. The product proved to be 1-aminopyrene (1-AP), based on its fluorescence spectrum, its mass spectrum, and its characteristic thin layer chromatographic and high performance liquid chromatographic patterns. The 1-NP nitroreductase activity of aerobic bacteria was low, but crude extracts from the anaerobic bacteria, i.e., Bacteroides fragilis, B. thetaiotaomicron, B. vulgatus, Fusobacterium mortiferum, F. nucleatum, Clostridium perfringens, C. sporogenes, Bifidobacterium adolescentis, B. bifidum, Eubacterium lentum, E. limosum, and Peptostreptococcus anaerobius, all easily converted 1-NP to 1-AP and proportionally decreased the mutagenic activity of 1-NP.