Cultures of Mycobacterium sp. strain PYR-1 were dosed with anthracene or phenanthrene and after 14 days of incubation had degraded 92 and 90% of the added anthracene and phenanthrene, respectively. The metabolites were extracted and identified by UV-visible light absorption, high-pressure liquid chromatography retention times, mass spectrometry, 1 H and 13 C nuclear magnetic resonance spectrometry, and comparison to authentic compounds and literature data. Neutral-pH ethyl acetate extracts from anthracene-incubated cells showed four metabolites, identified as cis-1,2-dihydroxy-1,2-dihydroanthracene, 6,7-benzocoumarin, 1-methoxy-2-hydroxyanthracene, and 9,10-anthraquinone. A novel anthracene ring fission product was isolated from acidified culture media and was identified as 3-(2-carboxyvinyl)naphthalene-2-carboxylic acid. 6,7-Benzocoumarin was also found in that extract. When Mycobacterium sp. strain PYR-1 was grown in the presence of phenanthrene, three neutral metabolites were identified as cis-and trans-9,10-dihydroxy-9,10-dihydrophenanthrene and cis-3,4-dihydroxy-3,4-dihydrophenanthrene. Phenanthrene ring fission products, isolated from acid extracts, were identified as 2,2-diphenic acid, 1-hydroxynaphthoic acid, and phthalic acid. The data point to the existence, next to already known routes for both gram-negative and gram-positive bacteria, of alternative pathways that might be due to the presence of different dioxygenases or to a relaxed specificity of the same dioxygenase for initial attack on polycyclic aromatic hydrocarbons.Anthracene and phenanthrene are tricyclic aromatic hydrocarbons that are found in high concentrations in polycyclic aromatic hydrocarbon (PAH)-contaminated sediments, surface soils, and waste sites. These hydrophobic contaminants are widely distributed in the environment, occurring as natural constituents of fossil fuels and their anthropogenic pyrolysis products (6,24,55). Unlike the higher-molecular-weight PAHs, phenanthrene and anthracene do not pose a risk to human health, since they exhibit no genotoxic or carcinogenic effects. However, they have been shown to be toxic to fish and algae (45,46). Anthracene and phenanthrene are considered prototypic PAHs and serve as signature compounds to detect PAH contamination, since their chemical structures are found in carcinogenic PAHs, such as benzo[a]pyrene and benz[a]anthracene. They have also been used as model PAHs to determine factors that affect the bioavailability, biodegradation potential, and rate of microbial degradation of PAHs in the environment (5,6,24,48).A variety of bacterial species have been isolated that have the ability to utilize anthracene or phenanthrene as the sole source of carbon and energy (6,33,48). The initial reactions in the degradation of anthracene and phenanthrene are catalyzed by multicomponent dioxygenases that incorporate both atoms of molecular oxygen into the PAH nucleus to produce cisdihydrodiols (1,22). Genes involved in PAH metabolism and its regulation have been described for Pseudomonas, Sphin...

The effects of pH on the growth of Mycobacterium vanbaalenii PYR-1 and its degradation of phenanthrene and pyrene were compared at pH 6.5 and pH 7.5. Various degradation pathways were proposed in this study, based on the identification of metabolites from mass and NMR spectral analyses. In tryptic soy broth, M. vanbaalenii PYR-1 grew more rapidly at pH 7.5 (mu'=0.058 h(-1)) than at pH 6.5 (mu'=0.028 h(-1)). However, resting cells suspended in phosphate buffers with the same pH values displayed a shorter lag time for the degradation of phenanthrene and pyrene at pH 6.5 (6 h) than at pH 7.5 (48 h). The one-unit pH drop increased the degradation rates four-fold. Higher levels of both compounds were detected in the cytosol fractions obtained at pH 6.5. An acidic pH seemed to render the mycobacterial cells more permeable to hydrophobic substrates. The major pathways for the metabolism of phenanthrene and pyrene were initiated by oxidation at the K-regions. Phenanthrene-9,10- and pyrene-4,5-dihydrodiols were metabolized via transient catechols to the ring fission products, 2,2'-diphenic acid and 4,5-dicarboxyphenanthrene, respectively. The metabolic pathways converged to form phthalic acid. At pH 6.5, M. vanbaalenii PYR-1 produced higher levels of the O-methylated derivatives of non-K-region phenanthrene- and pyrene-diols. Other non-K-region products, such as cis-4-(1-hydroxynaphth-2-yl)-2-oxobut-3-enoic acid, 1,2-dicarboxynaphthalene and benzocoumarin-like compounds, were also detected in the culture fluids. The non-K-region polycyclic aromatic hydrocarbon oxidation might be a significant burden to the cell due to the accumulation of toxic metabolites.

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Malachite green (MG), a triphenylmethane dye used to treat fungal and protozoan infections in fish, undergoes sequential oxidation to produce various N-demethylated derivatives (monodes-, dides(sym)-, dides(unsym)-, trides-, and tetrades-) both before and after reduction to leucomalachite green (LMG). The close structure resemblance of the metabolites with aromatic amine carcinogens implicates a potential genotoxicity from exposure to MG. The availability of the synthetic standards is important for metabolic and DNA adduct studies of MG. This paper describes a simple and versatile method for the synthesis of MG, LMG, and their N-demethylated metabolites. The synthesis involves a coupling of 4-(dimethylamino)benzophenone or 4-nitrobenzophenone with the aryllithium reagents derived from appropriately substituted 4-bromoaniline derivatives, followed by treatment with HCl in methanol. The resulting cationic MG and their leuco analogues showed systematic UV/vis spectral and tandem mass fragmentation patterns consistent with sequential N-demethylation. The extensive (1)H and (13)C spectral assignments of the metabolites were aided by the availability of (13)C(7)-labeled MG and LMG. The results indicate the existence of a resonance structure with the cationic charge located in the central methane carbon (C(7)). The synthetic procedure is general in scope so that it can be extended to the preparation of N-demethylated metabolites of other structurally related N-methylated triphenylmethane dyes.