Anthracene metabolites

The Intercalation of Benzo[a]pyrene and 7,12-Dimethylbenz[a]anthracene Metabolites and Metabolite Model Compounds into DNA... 

Physicochemical properties of several phenanthrene and anthracene metabolites... 

Ladics GS, Kawabata TT, White KL Jr. 1991. Suppression of the in vitro humoral immune response of mouse splenocytes by 7.12-dimethylbenz(a)anthracene metabolites and inhibition of immunosuppression by alpha-naphthoflavone. Toxicol Appl Pharmacol 110(1) 31-44. 

Aeruginosine A (254) (69JCS(C)2514) and B (255) (61MI2), shown in Scheme 83, are metabolites of the pyocyanine producing Pseudomonas aeruginosa. They are isoconjugate with the odd alternant 1-isopropenyl-anthracene anion (class 13). 

C]-anthracene was used to study its degradation in soil, and the formation of labeled metabolites that could be released only after alkaline hydrolysis (Richnow et al. 1998). It was possible to construct a carbon balance during the 599-d incubation, and to distinguish metabolically formed phthalate from indigenous phthalate in the soil. 

Metabolites may also play a role in the association of the substrate with humic and fulvic acid components. Two illustrations are given (a) naphth-l-ol, an established fungal metabolite of naphthalene, may play a role in the association of naphthalene with humic material (Burgos et al. 1996) and (b) it has been shown that C-labeled metabolites of [9- C]-anthracene including 2-hydroxyanthracene-3-carboxylate and phthalate were not extractable from soil with acetone or dichloromethane, and required alkaline hydrolysis for their recovery (Richnow et al. 1998). 

Whereas plausible fungal metabolites from anthracene, acenaphthylene, fluorene, and benz[fl]anthracene—anthracene-9,10-quinone, acenaphthene-9,10-dione, fluorene-9-one, and benz[fl]anthracene-7,12-quinone—were found transiently in compost-amended soil, these were formed even in sterile controls by abiotic reactions (Wischmann and Steinhart 1997). 

Research in PAH carcinogenesis has made major advances in the past decade. Most notable has been identification of diol epoxide metabolites as the active forms of benzo[a]pyrene, 7,12-dimethylbenz[tf]anthracene, and other carcinogenic PAH. This finding has stimulated enormous research activity and opened the way to determination of the detailed molecular mechanism of action of this important class of carcinogenic molecules. 

Methods for the synthesis of the biologically active dihydrodiol and diol epoxide metabolites of both carcinogenic and noncarcinogenic polycyclic aromatic hydrocarbons are reviewed. Four general synthetic routes to the trans-dihydrodiol precursors of the bay region anti and syn diol epoxide derivatives have been developed. Syntheses of the oxidized metabolites of the following hydrocarbons via these methods are described benzo(a)pyrene, benz(a)anthracene, benzo-(e)pyrene, dibenz(a,h)anthracene, triphenylene, phen-anthrene, anthracene, chrysene, benzo(c)phenanthrene, dibenzo(a,i)pyrene, dibenzo(a,h)pyrene, 7-methyl-benz(a)anthracene, 7,12-dimethylbenz(a)anthracene, 3-methylcholanthrene, 5-methylchrysene, fluoranthene, benzo(b)fluoranthene, benzo(j)fluoranthene, benzo(k)-fluoranthene, and dibenzo(a,e)fluoranthene. 

Figure 2. Reactive metabolites and metabolite model compounds derived from 7,12-dimethylbenz[a]anthracene.

The DMBA metabolite model compounds which have been examined include the benz[a]anthracene (BA) derivatives, 1,2,3,4-tetrahydro-BA 02, U), 5,6-dihydro-BA U2), and 8,9,10,11-tetrahydro-BA (12,... 

As presented in Table II, no quinones are obtained with NADPH for dibenz[a,h]anthracene and benz[a]anthracene, whereas with cumene hydroperoxide a trace amount of benz[a]anthracene quinone is observed. For the PAH with low IP, quinones are formed in the presence of both cofactors. The relationship between IP and formation of quinones constitutes further evidence that these metabolites are obtained by an initial one-electron oxidation of the PAH with formation of its radical cation. 

These findings indicate that PGH synthase in the presence of arachidonate can catalyze the terminal activation step in BP carcinogenesis and that the reaction may be general for dihydrodiol metabolites of polycyclic hydrocarbons. Guthrie et. al. have shown that PGH synthase catalyzes the activation of chrysene and benzanthracene dihydrodiols to potent mutagens (33). As in the case with BP, only the dihydrodiol that is a precursor to bay region diol epoxides is activated. We have recently shown that 3,4-dihydroxy-3,4-dihydro-benzo(a)anthracene is oxidized by PGH synthase to tetrahydrotetraols derived from the anti-diol epoxide (Equation 4) (34). 

Time elapsed after i C-anthracene addition, hr Fraction of total l C in form of water-soluble metabolites... 

We employed various substrates to check for MFO in two bivalve species, a salt water mussel (Mytilus edulis) and a fresh water clam (Anodonta sp). Cytochrome P-450 was also studied. Organisms were exposed to 100 PPM Venezuelan crude in a stagnant system for up to one month. Enzyme assays were carried out with digestive gland 9000 g homogenates (17) and cytochrome P-450 analysis, with microsomes (21). The hydrocarbon substrates investigated included 1I+C-labelled benzo(a)pyrene, fluorene, anthracene, and naphthalene. The method used for separation of BP metabolites by thin layer radiochromatography has been described (7). The metabolite detection method for the other aromatic hydrocarbons was essentially the same except methylene chloride was used as metabolite extractant as well as TLC developer. Besides the hydrocarbon substrates, we also checked for other MFO reactions, N-dealkylase with C-imipramine (22) and 0-dealkylase with ethoxycoumarin (15). 

A strain of Beijerinckia oxiAizeA benzo [a] anthracene producing l -hydroxy-2-anthranoic acid as the major product. Three other metabolites identified were 2-hydroxy-3-phenanthroic acid, 3-hydroxy-2-phenanthroic acid, and c7s-l,l-dihydroxy-l,2-dihydrobenzo[a]anthracene (Gibson et al, 1975 Mahaffey et ah, 1988). 

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