Anaerobic aniline degradation via reductive deamination of 4-aminobenzoyl-CoA in Desulfobacterium anilini

The initial reactions involved in anaerobic aniline degradation by the sulfate-reducing Desulfobacterium anilini were studied. Experiments for substrate induction indicated the presence of a common pathway for aniline and 4-aminobenzoate, different from that for degradation of 2-aminobenzoate, 2-hydroxybenzoate, 4-hydroxybenzoate, or phenol. Degradation of aniline by dense cell suspensions depended on CO₂ whereas 4-aminobenzoate degradation did not. If acetyl-CoA oxidation was inhibited by cyanide, benzoate accumulated during degradation of aniline or 4-aminobenzoate, indicating an initial carboxylation of aniline to 4-aminobenzoate, and further degradation via benzoate of both substrates. Extracts of alinine or 4-aminobenzoategrown cells activated 4-aminobenzoate to 4-aminobenzoyl-CoA in the presence of CoA, ATP and Mg²⁺. 4-Aminobenzoyl-CoA-synthetase showed a K _m for 4-aminobenzoate lower than 10 M and an activity of 15.8 nmol · min^-1 · mg^-1. 4-Aminobenzoyl-CoA was reductively deaminated to benzoyl-CoA by cell extracts in the presence of low-potential electron donors such as titanium citrate or cobalt sepulchrate (2.1 nmol · min^-1 · mg^-1). Lower activities for the reductive deamination were measured with NADH or NADPH. Reductive deamination was also indicated by benzoate accumulation during 4-aminobenzoate degradation in cell suspensions under sulfate limitation. The results provide evidence that aniline is degraded via carboxylation to 4-aminobenzoate, which is activated to 4-aminobenzoyl-CoA and further metabolized by reductive deamination to benzoyl-CoA.     

Mechanisms and pathways of aniline elimination from aquatic environments.

The fate of aniline, a representative of arylamine pollutants derived from the manufacture of dyes, coal liquefaction, and pesticide degradation, was comprehensively evaluated by use of unpolluted and polluted pond water as model environments. Evaporation plus autoxidation proved to be minor elimination mechanisms, removing ca. 1% of the added aniline per day. Instantaneous binding to humic components of a 0.1% sewage sludge inoculum removed 4%. Biodegradation of aniline in pond water was accelerated by the sewage sludge inoculum. A substantial portion of the degraded aniline carbon was mineralized to CO2 within a 1-week period, and microbial biomass was formed as a result of aniline utilization. Biodegradation was clearly the most significant removal mechanism of polluting aniline from pond water. A gas chromatographic-mass spectrometric analysis of biodegradation intermediates revealed that the major pathway of aniline biodegradation in pond water involved oxidative deamination to catechol, which was further metabolized through cis,cis-muconic, beta-ketoadipic, levulinic, and succinic acid intermediates to CO2. Minor biodegradation pathways involved reversible acylation to acetanilide and formanilide, whereas N-oxidation resulted in small amounts of oligomeric condensation products.     

Mechanisms and pathways of aniline elimination from aquatic environments

The fate of aniline, a representative of arylamine pollutants derived from the manufacture of dyes, coal liquefaction, and pesticide degradation, was comprehensively evaluated by use of unpolluted and polluted pond water as model environments. Evaporation plus autoxidation proved to be minor elimination mechanisms, removing ca. 1% of the added aniline per day. Instantaneous binding to humic components of a 0.1% sewage sludge inoculum removed 4%. Biodegradation of aniline in pond water was accelerated by the sewage sludge inoculum. A substantial portion of the degraded aniline carbon was mineralized to CO2 within a 1-week period, and microbial biomass was formed as a result of aniline utilization. Biodegradation was clearly the most significant removal mechanism of polluting aniline from pond water. A gas chromatographic-mass spectrometric analysis of biodegradation intermediates revealed that the major pathway of aniline biodegradation in pond water involved oxidative deamination to catechol, which was further metabolized through cis,cis-muconic, beta-ketoadipic, levulinic, and succinic acid intermediates to CO2. Minor biodegradation pathways involved reversible acylation to acetanilide and formanilide, whereas N-oxidation resulted in small amounts of oligomeric condensation products.     

Investigation on the regulation of aniline utilization in Pseudomonas multivorans strain An 1

Summary Pseudomonas multivorans strain An 1 was isolated from forest soil after enrichment in a medium containing 0.1% aniline as the sole source of carbon and energy. Increasing aniline concentrations increasingly inhibited bacterial growth. At pH 7, aniline concentrations greater than 16mM were toxic enough to completely arrest growth. The optimal pH for growth on aniline was 6.5.On binary mixtures of aniline and additional carbon sources, diauxic growth was observed. The addition carbon sources caused various degrees of repression of the aniline catabolizing enzyme system. The fastest induction of this system occurred at pH 4, suggesting that protonization of the aniline molecule is crucial.     

Characterization of a Pseudomonas sp. Capable of Aniline Degradation in the Presence of Secondary Carbon Sources

Pseudomonas strain K1 is a gram-negative rod which grows aerobically on minimal media containing aniline with a doubling time of 2 h at 30°C. The half-saturation parameter for aniline metabolism by aniline-grown cells was 3.8 μmol · liter⁻¹. Concentrations of aniline as low as 50 nM were metabolized. Neither substituted anilines nor other aromatic compounds (other than aromatic amino acids) supported growth. Cells grew as fast on aniline as on nonaromatic substrates such as lactate. The aromatic ring was cleaved via the meta pathway. Catechol 2,3-oxygenase activity was induced by aniline, even in cultures containing alternative carbon sources such as lactate. Cultures grown on a mixture of aniline and lactate mineralized aniline in the presence of the second substrate. Lactate-grown cultures lacked catechol oxygenase activity, and resting cells from these cultures did not respire aniline. Resting cells from aniline-grown cultures exhibited high respiratory activity upon the addition of aniline or catechol, some activity with toluidine, and no activity after addition of a wide variety of other aromatic compounds, including dihydroxybenzylamine, chloroanilines, ethylanilines, aminophenols, aminobenzoates, and dihydroxybenzoates. Although substituted anilines were not metabolized, 3-or 4-chloroaniline did induce the enzymes for aniline oxidation.     

食酸丛毛单胞菌AN3菌株降解苯胺代谢途径的研究

食酸丛毛单胞菌(\%Comamonas acidovorans\%)AN3菌株中降解苯胺的酶类均为诱导酶,在以苯胺为唯一碳、氮源和能源生长的细胞中,含有苯胺双加氧酶、邻苯二酚2,3双加氧酶、2羟基己二烯半醛酸脱氢酶、4草酰巴豆酸脱羧酶和4羟基2酮戊酸醛缩酶等。苯胺双加氧酶作用于苯胺的\%K\%m值和\%V\%\-\{max\}分别为292μmol/L和3.57μmol\5mg\+\{-1\}·min-1;邻苯二酚2,3双加氧酶作用于邻苯二酚的\%K\%m和\%V\%\-\{max\}分别为16.4 mol/L和15.2μmol\5mg\+\{-1\}\5min\+\{-1\}。根据实验结果,推测了该菌株降解苯胺的代谢途径。     

Characterization of the nitrobenzene-degrading strain Pseudomonas sp. a3 and use of its immobilized cells in the treatment of mixed aromatics wastewater

A bacterial strain Pseudomonas sp. a3 capable of degrading nitrobenzene, phenol, aniline, and other aromatics was isolated and characterized. When nitrobenzene was degraded, the release of NH(4) (+) was detected, but not of NO(2) (-). This result implied that nitrobenzene might have a partial reductive metabolic pathway in strain a3. However, aniline appeared as one of the metabolites during the aerobic degradation of nitrobenzene. Moreover, the appearance of 2-aminophenol during aniline degradation by strain a3 indicated that novel initial reactions existed during the degradation of nitrobenzene and aniline by strain a3. Strain a3 was immobilized in the mixed carrier of polyvinyl alcohol and sodium alginate to improve its degrading efficiency. The optimal concentrations of polyvinyl alcohol and sodium alginate in the mixed carrier were 9 and 3 %, respectively. The immobilized cells had stable degradation activity and good mechanical properties in the recycling tests. The immobilized cells also exhibited higher tolerances in acidic (pH 4-5) and highly saline (10 % NaCl) environments than those of free cells. The biodegradation of nitrobenzene mixed with aniline and phenol using immobilized cells of Pseudomonas sp. a3 was also greatly improved compared with those of free cells. The immobilized cells could completely degrade 300 mg L(-1) nitrobenzene within 10 h with 150 mg L(-1) aniline and 150 mg L(-1) phenol. This result revealed that the immobilized cells of Pseudomonas sp. a3 could be a potential candidate for treating nitrobenzene wastewater mixed with other aromatics.     

Microbial mineralization of ring-substituted anilines through an ortho-cleavage pathway

Moraxella sp. strain G is able to utilize as sole source of carbon and nitrogen aniline, 4-fluoroaniline, 2-chloroaniline, 3-chloroaniline, 4-chloroaniline (PCA), and 4-bromoaniline but not 4-iodoaniline, 4-methylaniline, 4-methoxyaniline, or 3,4-dichloroaniline. The generation time on PCA was 6 h. The pathway for the degradation of PCA was investigated by analysis of catabolic intermediates and enzyme activities. Mutants of strain G were isolated to enhance the accumulation of specific pathway intermediates. PCA was converted by an aniline oxygenase to 4-chlorocatechol, which in turn was degraded via a modified ortho-cleavage pathway. Synthesis of the aniline oxygenase was inducible by various anilines. This enzyme exhibited a broad substrate specificity. Its specific activity towards substituted anilines seemed to be correlated more with the size than with the electron-withdrawing effect of the substituent and was very low towards anilines having substituents larger than iodine or a methyl group. The initial enzyme of the modified ortho-cleavage pathway, catechol 1,2-dioxygenase, had similar characteristics to those of corresponding enzymes of pathways for the degradation of chlorobenzoic acid and chlorophenol, that is, a broad substrate specificity and high activity towards chlorinated and methylated catechols.     

Comparative studies of sheep liver and lung microsomal aniline 4-hydroxylase

1. The specific activity of the aniline 4-hydroxylase which catalyses hydroxylation of aniline to p-aminophenol was found to be 0.65 (N = 10) and 0.15 (N = 13) nmol p-aminophenol formed/mg protein/min, in sheep liver and lung microsomes, respectively. 2. The effects of aniline concentration, pH, cofactors, amount of enzyme and incubation period, on enzyme activity were studied, and the optimum conditions for maximum activity of liver and lung microsomes were determined. 3. Liver and lung microsomal aniline 4-hydroxylase activity was found to be completely dependent on the presence of cofactor NADPH. 4. The Lineweaver Burk and Eadie Hofstee plots of the liver enzyme were found to be curvilinear, suggesting that the enzyme did not follow the Michaelis Menten kinetics. From these graphs, two different Km values were calculated for the liver enzyme as 3.21 and 0.072 mM aniline. Km of the lung enzyme was calculated to be 1.43 mM aniline from its Lineweaver Burk graph. 5. The effects of magnesium, nickel and cadmium ions on the liver and lung aniline 4-hydroxylase activity were examined. Magnesium ion was found to have stimulatory effect, whereas nickel and cadmium ions inhibited the activity of the both liver and lung enzyme.     

Increased oxidation of p-nitrophenol and aniline by intact hepatocytes isolated from pyrazole-treated rats

Induction of cytochrome P-450 IIE1 by pyrazole has been shown in a variety of studies with isolated microsomes or reconstituted systems containing the purified P-450 isozyme. Experiments were conducted to document induction by pyrazole in intact hepatocytes by studying the oxidation of p-nitrophenol to 4-nitrocatechol or of aniline to p-aminophenol. Hepatocytes prepared from rats treated with pyrazole for 2 days oxidized p-nitrophenol or aniline at rates which were 3- to 4-fold higher than saline controls. To observe maximal induction in hepatocytes, it was necessary to add metabolic substrates such as pyruvate, sorbitol or xylitol, which suggests that availability of the NADPH cofactor may be rate-limiting in the hepatocytes from the pyrazole-treated rats. Carbon monoxide inhibited the oxidation of p-nitrophenol and aniline by hepatocytes from the pyrazole-treated rats and controls, demonstrating the requirement for cytochrome P-450. The oxidation of both substrates by the hepatocyte preparations was inhibited by a variety of agents that interact with and are effective substrates for oxidation by P-450 IIE1 such as ethanol, dimethylnitrosamine, pyrazole and 4-methylpyrazole. Microsomes isolated from pyrazole-treated rats oxidized aniline and p-nitrophenol at elevated rats compared to saline controls. These results indicate that induction by pyrazole of the oxidation of drugs which are effective substrates for P-450 IIE1 can be observed in intact hepatocytes. The extent of induction and many of the characteristics of aniline or p-nitrophenol oxidation observed with isolated microsomes from pyrazole-treated rats can also be found in the intact hepatocytes.     

Microbial mineralization of ring-substituted anilines through an ortho-cleavage pathway.

Moraxella sp. strain G is able to utilize as sole source of carbon and nitrogen aniline, 4-fluoroaniline, 2-chloroaniline, 3-chloroaniline, 4-chloroaniline (PCA), and 4-bromoaniline but not 4-iodoaniline, 4-methylaniline, 4-methoxyaniline, or 3,4-dichloroaniline. The generation time on PCA was 6 h. The pathway for the degradation of PCA was investigated by analysis of catabolic intermediates and enzyme activities. Mutants of strain G were isolated to enhance the accumulation of specific pathway intermediates. PCA was converted by an aniline oxygenase to 4-chlorocatechol, which in turn was degraded via a modified ortho-cleavage pathway. Synthesis of the aniline oxygenase was inducible by various anilines. This enzyme exhibited a broad substrate specificity. Its specific activity towards substituted anilines seemed to be correlated more with the size than with the electron-withdrawing effect of the substituent and was very low towards anilines having substituents larger than iodine or a methyl group. The initial enzyme of the modified ortho-cleavage pathway, catechol 1,2-dioxygenase, had similar characteristics to those of corresponding enzymes of pathways for the degradation of chlorobenzoic acid and chlorophenol, that is, a broad substrate specificity and high activity towards chlorinated and methylated catechols.     

Accleration of autooxidation of human oxyhemoglobin by aniline and its relation to hemoglobin-catalyzed aniline hydroxylation.

Changes in the ultraviolet/visible spectrum of human oxyferrohemoglobin upon addition of aniline were indicative of a concentration-dependent interaction of aniline with hemoglobin, resulting in accelerated autooxidation of the hemoprotein. Oxygen was found to markedly inhibit this interaction of aniline with oxyhemoglobin. The dependence of the rate of autooxidation on aniline concentration followed saturation kinetics and showed a half-maximal response at 8 mM aniline. This value is equal to the value of Km for aniline as substrate for the O2-dependent, hemoglobin-catalyzed hydroxylation reaction which yields p-aminophenol (Mieyal, J. J., Ackerman, R.S., Blumer, J.L., and Freeman, L.S. (1976) J. Biol. Chem. 241, 3436-3441). Thus, an aniline-oxyhemoglobin complex is implicated in the overall catalytic reaction. No detectable p-aminophenol was formed when aniline was combined with oxyhemoglobin in the absence of an electron donor, but hydroxylation of aniline does occur when NADPH, NADPH plus P-450 reductase, or Na2S2O4 are also added.     

Aerobic versus anaerobic metabolism of halogenated anilines by aParacoccus sp.

AParacoccus sp. which transforms aniline and different halogen-substituted derivatives under aerobic and anaerobic conditions was isolated from the soil. In experiments with¹⁴C-ring-labeled 4-chloroaniline, approximately 60% of the radioactive material disappeared from the growth medium after incubation under anaerobiosis within 48 hr, but under aerobic conditions no decrease of radioactivity in the growth medium was observed, although 4-chloroaniline was completely metabolized. Acetylation appears to constitute, especially under aerobic conditions, a major transformation mechanism by the bacterium, since almost 50% of the acetylated compound could be detected and identified if aniline, 2-, 3-, and 4-chloroaniline served as substrate. The formation of different metabolites under aerobic and anaerobic conditions clearly indicates the existence of two separate pathways in the metabolism of aniline compounds depending on the oxygen status of the environment.     

Up-regulation of heme oxygenase-1 in rat spleen after aniline exposure

The splenic toxicity of aniline is characterized by vascular congestion, hyperplasia, fibrosis, and the development of a variety of sarcomas in rats. However, the underlying mechanisms by which aniline elicits splenotoxic response are not well understood. Previously we have shown that aniline exposure causes oxidative damage to the spleen. To further explore the oxidative mechanism of aniline toxicity, we evaluated the potential contribution of heme oxygenase-1 (HO-1), which catalyzes heme degradation and releases free iron. Male SD rats were given 1 mmol/kg/day aniline in water by gavage for 1, 4, or 7 days, and respective controls received water only. Aniline exposure led to significant increases in HO-1 mRNA expression in the spleen (2-and 2.4-fold at days 4 and 7, respectively) with corresponding increases in protein expression, as confirmed by ELISA and Western blot analysis. Furthermore, immunohistochemical assessment of spleen showed stronger immunostaining for HO-1 in the spleens of rats treated for 7 days, confined mainly to the red pulp areas. No changes were observed in mRNA and protein levels of HO-1 after 1 day exposure. The increase in HO-1 expression was associated with increases in total iron (2.4-and 2.7-fold), free iron (1.9-and 3.5-fold), and ferritin levels (1.9-and 2.1-fold) at 4 and 7 days of aniline exposure. Our data suggest that HO-1 up-regulation in aniline-induced splenic toxicity could be a contributing pro-oxidant mechanism, mediated through iron release, and leading to oxidative damage.     

Degradation of aniline and monochloroanilines by Rhodococcus sp. An 117 and a pseudomonad: a comparative study

Two newly isolated aniline-degrading bacterial strains were characterized with regard to their enzyme systems responsible for aniline catabolism. One of them identified as a Rhodococcus sp. metabolized aniline exclusively via the beta-ketoadipate pathway by means of inducible enzymes. The aniline-degrading enzyme system of the second isolate, presumably a pseudomonad, was shown to consist of an inducible aniline-converting enzyme and constitutive meta-pathway enzymes. Both isolates failed to metabolize monochlorinated anilines in the absence of additional carbon sources. To explain this the ring-cleaving enzymes of both isolates were examined for their substrate specificities. Furthermore, the effect of 4-chlorocatechol on the enzymes catalyzing aniline conversion and catechol oxygenation was investigated.     

The genotoxicity of a variety of aniline derivatives in a DNA repair test with primary cultured rat hepatocytes

The genotoxicity of a variety of aniline derivatives was examined by a DNA repair test with rat hepatocytes. Out of 37 aniline derivatives, 6 chemicals, i.e., 2,4,6-trimethylaniline (mesidine), 2,4-xylidine, 3,5-diaminobenzoic acid, 3,4-diaminochlorobenzene, 2-chloro-4-methylaniline and 4-chloro-N-methylaniline, elicited positive DNA repair responses. The results are in agreement with the bacterial mutagenicities with or without norharman of these compounds. Positive compounds of unknown carcinogenicity in the present assay, i.e., 3,5-diaminobenzoic acid, 2-chloro-4-methylaniline and 4-chloro-N-methylaniline are suspected of being potentially carcinogenic.     

Aniline hydroxylase activities of haemoglobin: Kinetics and mechanism

The mechanism of the aniline hydroxylase activity of methaemoglobin in a monooxygenase system consisting of NADH as electron donor, riboflavin, FAD, FMN or methylene blue as electron carrier and methaemoglobin as the terminal oxidase has been studied. Hydrogen peroxide is produced from oxygen in a methaemoglobin-independent process. 4-Aminophenol is subsequently produced peroxidatively by an NADH-dependent process; NADH prevents a further oxidation of 4-aminophenol in the presence of haemoglobin. In the absence of electron carrier, NADH slowly reduces haemoglobin and then oxyhaemoglobin reacts with aniline to give 4-aminophenol. In the absence of electron donor and electron carrier, oxyhaemoglobin and aniline give rise to the reversible production of 4-aminophenol.     

Degradation of aniline and monochlorinated anilines by soil-born Pseudomonas acidovorans strains

Four bacterial strains (CA26, CA28, CA37, and CA45), which all were able to use aniline, 3-chloroaniline (3-CA), and 4-chloroaniline (4-CA) as sole sources of carbon, nitrogen and energy, were isolated after enrichment in aerated soil columns and identified as Pseudomonas acidovorans strains. In addition strains CA26 and CA45 were able to degrade 2-chloroaniline (2-CA) at very low rates. At 25°C strain CA28 was grown on aniline and 3-CA with generation times of 3.0 and 7.7 h, respectively, and exhibited complete mineralization of these substrates in degradation rates of 2.25 mmol aniline and 1.63 mmol 3-CA g^-1 of biomass per hour, respectively. Degradation of 4-CA occurred at 1.54 mmol 4-CA g^-1 of biomass per hour and a generation time of 18.7 h but, in contrast, was not complete due to formation of minor amounts of chlorohydroxymuconic semialdehyde, a meta-cleavage product of 4-chlorocatechol. The initial attack on the substrate, the formation of corresponding chlorocatechols from 3-CA and 4-CA, was found to be the rate-limiting degradation step. Evidence for two different aniline-oxygenase systems in strain CA28 with distinct activity pattern on chlorinated and nonsubstituted anilines was demonstrated by oxygen uptake rate experiments with aniline and chloroaniline pregrown cells. Further degradation was shown to be initialized by catechol dioxygenases.Non-standard abbreviations CA chloroaniline - DCA dichloroaniline - ECM enrichment and cultivation medium - CFU colony forming unit     

Degradation of aniline by newly isolated,extremely aniline-tolerant <Emphasis Type="Italic">Delftia </Emphasis>sp. AN3

A bacterial strain, AN3, which was able to use aniline or acetanilide as sole carbon, nitrogen and energy sources was isolated from activated sludge and identified as Delftiasp. AN3. This strain was capable of growing on concentrations of aniline up to 53.8 mM (5000 mg/l). Substituted anilines such as N-methylaniline, N, N-dimethylaniline, 2-methylaniline, 4-methylaniline, 2-chloroaniline, 3-chloroaniline, o-aminoaniline, m-aminoaniline, p-aminoaniline, and sulfanilic acid did not support the growth of strain AN3. The optimal temperature and pH for growth and degradation of aniline were 30 degrees C and 7.0, respectively. The activities of aniline dioxygenase, catechol 2,3-dioxygenase and other enzymes involved in aniline degradation were determined, and results indicated that all of them were inducible. The K (m) and V (max) of aniline dioxygenase were 0.29 mM and 0.043 mmol/mg protein/min, respectively. The K (m) and V (max) of catechol 2, 3-dioxygenase for catechol were 0.016 mM and 0.015 mmol/mg protein/min, respectively. Based on the results obtained, a pathway for the degradation of aniline by Delftiasp. AN3 was proposed. The importance of the strain to the operation of municipal wastewater treatment plants is discussed.     

On the inhibition of microsomal drug metabolism by polychlorinated biphenyls (PCB) and related phenolic compounds.

The in vitro metabolism of p-nitroanisole, aminopyrine, and aniline by rat liver microsomal monoxygenases were studied in the presence of different polychlorinated biphenyl (PCB) mixtures and some related hydroxybiphenyls. The tested PCB mixtures contained preferably dichloro- (di-CB), tetrachloro- (tetra-CB), or hexachlorobiphenyls (hexa-CB). All PCB were competitive inhibitors of only aminopyrine demethylation by normal microsomes (Ki 22-39 micron). In microsomes of PCB-pretreated rats the aminopyrine demethylation was inhibited noncompetitively by di-CB and hexa-CB whereas tetra-CB remained a competitive inhibitor (Ki 12 micron). Moreover, after PCB pretreatment all PCB were competitive inhibitors of p-nitroanisole demethylation. 2-OH-biphenyl and 4-OH-biphenyl caused competitive inhibition of aminopyrine demethylation and aniline hydroxylation but failed to inhibit p-nitroanisole metabolism by normal microsomes. Chlorinated 4-hydroxybiphenyls inhibited competitively the metabolism of both type I and type II substrates. However, after PCB pretreatment all phenolic compounds caused uncompetitive inhibition of aniline hydroxylation.