Microsomal metabolism of dibenz[a,c]anthracene, dibenz[a,h]anthracene and dibenz[a,j]anthracene to bis-dihydrodiols and polyhydroxylated products

Polar, ethyl acetate soluble metabolites formed in incubations of dibenz[a,c]-anthracene (DB[a,c]A), dibenz[a,h]anthracene (DB[a,h]A) and the related DB[a,h]A 3,4-diol and dibenz[a,j]anthracene (DB[a,j]A) with 3-methylcholanthrene (3-MC)-induced rat liver microsomal preparations have been separated by HPLC and examined using fluorescence, UV and NMR spectroscopy. Metabolites with spectral properties consistant with their identification as the 3,4:8,9-bis-diol of DB[a,j]A and a 1,2,3,4,12,13-hexol derived from DB[a,c]A were found. DB[a,h]A was metabolized to three polar products identified as the 3,4:10,11-bis-diol and the related 1,2,3,4,8,9- and 1,2,3,4,10,11-hexols, which were also formed, together with the related 1,2,3,4-tetrol, from the DB[a,h]A 3,4-diol. The possible role of bis-diols in the metabolic activation of these three dibenzanthracenes is discussed.     

The induction of sister-chromatid exchanges in Chinese hamster ovary cells by K-region epoxides and some dihydrodiols derived from benz[a]anthracene, dibenz[a,c]anthracene and dibenz[a,h]anthracene

Experiments were performed to investigate the effects of 3 polycyclic aromatic hydrocarbons, benz[a]anthracene, dibenz[a,c]anthracene and dibenz[a,h]anthracene and K-regio epoxides and some of their related dihydrodiols on the chromosomes of Chinese hamster ovary cells in vitro. Of the 3 hydrocarbons only benz[a]anthracene showed any activity in inducing sister-chromatid exchanges. The K-region epoxide and the 3,4-dihydrodiol have been found to be more active than the corresponding K-region or the other non K-region dihydrodiols derived from benz[a]anthracene. Athough dibenz[a,c]anthracene was almost inactive, the K-region 5,6-epoxide and all 3 possible dihydrodiols, the 1,2-, 3,4- and 10,11-diols were active in inducing increased numbers of sister-chromatid exchanges in the chromosomes of these cells. The 3,4-dihydrodiol of dibenz[a,h]anthrecene was also active in inducing sister-chromatid exchanges whereas the 1,2- and 5,6-dihydrodiols were only weakly active. This study provides some support for the suggestiion that the activation of these 3 hydrocarbons proceeds by the metabolic conversion of non K-region dihydrodiols into vicinal diol-epoxides.     

P-Postlabeling high-performance liquid chromatographic improvements to characterize DNA adduct stereoisomers from benzo[a]pyrene and benzo[c]phenanthrene, and to separate DNA adducts from 7,12-dimethylbenz[a]anthracene

Single compounds can generate complex DNA adduct patterns by reactions through different pathways, with different target nucleotides and through different configurations of the products. DNA adduct analysis by ³²P-HPLC was improved by adding an isocratic plateau in an otherwise linear gradient, thereby enhancing resolution of predictable retention time intervals. This enhanced ³²P-HPLC technique was used to analyze and at least partly resolve 14 out of 16 available benzo[c]phenanthrene deoxyadenosine and deoxyguanosine adduct standards, 8 out of 8 available benzo[a]pyrene deoxyadenosine and deoxyguanosine adduct standards, and 51 peaks from 7,12-dimethylbenz[a]anthracene-calf thymus DNA reaction products. The same type of gradient modifications could be used to enhance resolution in analyses of other complex DNA adduct mixtures, e.g., in vivo in humans.     

Degradation of fluoranthene, pyrene, benz[a]anthracene and dibenz[a,h]anthracene by Burkholderia cepacia

Microbiological analysis of soils from a polycyclic aromatic hydrocarbon (PAH)-contaminated site resulted in the enrichment of five microbial communities capable of utilizing pyrene as a sole carbon and energy source. Communities 4 and 5 rapidly degraded a number of different PAH compounds. Three pure cultures were isolated from community 5 using a spray plate method with pyrene as the sole carbon source. The cultures were identified as strains of Burkholderia ( Pseudomonas ) cepacia on the basis of biochemical and growth tests. The pure cultures (VUN 10 001, VUN 10 002 and VUN 10 003) were capable of degrading fluorene, phenanthrene and pyrene (100 mg l⁻¹) to undetectable levels within 7–10 d in standard serum bottle cultures. Pyrene degradation was observed at concentrations up to 1000 mg l⁻¹. The three isolates were also able to degrade other PAHs including fluoranthene, benz[ a ]anthracene and dibenz[ a , h ]anthracene as sole carbon and energy sources. Stimulation of dibenz[ a , h ]anthracene and benzo[ a ]pyrene degradation was achieved by the addition of small quantities of phenanthrene to cultures containing these compounds. Substrate utilization tests revealed that these micro-organisms could also grow on n -alkanes, chlorinated- and nitro-aromatic compounds.     

The metabolism of benz[a]anthracene and dibenz[a,h]anthracene and their 5,6-epoxy-5,6-dihydro derivatives by rat-liver homogenates

1. Benz[a]anthracene was hydroxylated by rat-liver homogenates on the 3,4-,5,6- or 8,9-bond to yield phenols and dihydrodihydroxy compounds. Metabolic action at the 7- and 12-positions was also detected. 5,6-Epoxy-5,6-dihydrobenzanthracene was converted into a phenol that is probably 5-hydroxybenzanthracene and 5,6-dihydro-5,6-dihydroxybenzanthracene. Both substrates yielded a product that is probably S-(5,6-dihydro-6-hydroxy-5-benzanthracenyl)glutathione. 2. Dibenz[a,h]anthracene was hydroxylated by rat-liver homogenates to yield products that are probably 3- and 4-hydroxydibenzanthracene, 1,2-dihydro-1,2-dihydroxydibenzanthracene, 3,4-dihydro-3,4-dihydroxydibenzanthracene and 5,6-dihydro-5,6-dihydroxydibenzanthracene. There was no evidence for metabolic action at the 7- and 14-positions. 5,6-Epoxy-5,6-dihydrodibenzanthracene was converted into a phenol that is probably 5-hydroxydibenzanthracene and 5,6-dihydro-5,6-dihydroxydibenzanthracene. Both substrates yielded a glutathione conjugate that is probably S-(5,6-dihydro-6-hydroxy-5-dibenzanthracenyl)glutathione. 3. The synthesis of 5,6-epoxy-5,6-dihydrodibenzanthracene is described and the reactions of this epoxide and 5,6-epoxy-5,6-dihydrobenzanthracene with water and thiols have been investigated. 4. The oxidation of dibenzanthracene in the ascorbic acid-Fe(2+) ion-oxygen model system is described.     

Induction of sister-chromatid exchanges in Chinese hamster ovary cells treated in vitro with non-k-region dihydrodiols of 7-methylbenz[a]anthracene and benzo[a]pyrene

Studies were carried out on the incidence of sister-chromatid exchanges induced in Chinese hamster ovary cells by in vitro treatment with the polycyclic aromatic hydrocarbons 7-methylbenz[a]anthracene and benzo[a]pyrene and with related K-region and non-K-region dihydrodiols. Appreciable increases in the incidence of sister-chromatid exchanges were apparent in cells treated with non-K-region dihydrodiols: the most active compounds were 3,4-dihydro-3,4-dihydroxy-7-methylbenz[a]anthracene and 7,8-dihydro-7,8-dihydroxybenzo[a]pyrene and the effects were dose-dependent. The parent hydrocarbons and the related K-region dihydrodiols induced some sister-chromatid exchanges but they were considerably less active than these two non-K-region diols. The results suggest that this system may usefully be applied to studies aimed at determining which dihydrodiols are important in the metabolic activation of the carcinogenic polycyclic hydrocarbons. These and other results also infer that Chinese hamster ovary cells possess some intrinsic ability to metabolize such compounds in the absence of exogenous activation systems.     

Bioalkylation of dibenz[a,b]anthracene in rat liver cytosol

Previous studies by other investigators have established that L-region methyl derivatives of dibenz[a,h]anthracene (DBA) were more carcinogenic than the parent hydrocarbon. The bioalkylation of DBA was investigated by incubating the hydrocarbon with rat liver cytosol fortified with S-adenosyl-L-methionine (SAM) in 0.1 M phosphate buffer (pH 7.4) for 1 h at 37 degrees C in air. The reaction was stopped by the addition of cold acetone and the mixture extracted with ethyl acetate and washed with water. The organic phase was evaporated and the residue dissolved in methylene chloride for analysis by reverse phase high performance liquid chromatography (HPLC) and gas chromatography/mass spectroscopy GC/MS. Products were found that were indistinguishable from 7-methyl-DBA and 7,14-dimethyl-DBA, 7-hydroxymethyl-DBA, 7-hydroxymethyl-14-methyl-DBA, and 7,14-dihydroxymethyl-DBA. The results suggest that unsubstituted carcinogenic hydrocarbons are preprocarcinogens that react with SAM in liver cytosol preparations, to form alkyl substituted procarcinogens, which are more potent than the corresponding preprocarcinogens.     

The formation of dihydrodiols in the chemical or enzymic oxidation of dibenz[a,c]anthracene, dibenz[a,h]-anthracene and chrysene.

The formation of trans-dihydrodiols from dibenz[a,c]anthracene, dibenz[a,h]anthracene and chrysene by chemical oxidation in an ascorbic acid-ferrous sulphate-EDTA system and by rat-liver microsomal fractions has been studied using a combination of thin-layer (TLC) and high pressure liquid chromatography (HPLC) to separate the mixtures of isomeric dihydrodiols. The 1,2- and 3,4-dihydrodiols of dibenz[a,c]anthracene, the 1,2-,3,4- and 5,6-dihydrodiols of dibenz[a,h]anthracene and the 1,2-, 3,4- and 5,6-dihydrodiols of chrysene were formed in chemical oxidations. These dihydrodiols were also formed when the three parent hydrocarbons were metabolized by rat-liver microsomal fractions and, in addition, dibenz[a,c]anthracene yielded the 10,11-dihydrodiol. The 1,2- and 3,4-dihydrodiols of dibenz[a,c]anthracene have not been reported previously either as metabolites of the hydrocarbon or as products of chemical syntheses and the 5,6-dihydrodiol of chrysene was not detected in earlier metabolic studies.     

Unusual patterns of benzo[a]pyrene metabolites and DNA-benzo[a]pyrene adducts produced by human placental microsomes in vitro

Human placental microsomes were incubated with [³H]benzo[a]pyrene (BP) and Salmon sperm DNA and the resulting metabolite-nucleoside complexes resolved by Sephadex LH-20 chromatography. The metabolite pattern was analyzed by high-pressure liquid chromatography (HPLC). The incubates were also co-chromatographed with extracts obtained from incubates with rat liver microsomes and [¹⁴C]BP. Phenols, quinones and 7,8-dihydrodiol were detected in the placental incubates. Both 9,10- and 4,5-dihydrodiols were very low as compared with control rat liver samples. Placental microsomes catalyzed the binding of BP metabolites to DNA in vitro, giving rise to two main complexes which co-chromatographed with rat liver-produced peaks attributable to 7,8-diol-9,10-epoxide and 7,8-oxide and/or quinones when metabolized further. The nucleoside metabolite peaks attributable to 4,5-oxide and 9-phenol-4,5-oxide were lacking when compared with the binding pattern catalyzed by rat liver. Both the total binding and specific metabolite-nucleoside adducts in the placenta correlated with fluorometrically measured aryl hydrocarbon hydroxylase (AHH) activity and with the amount of dihydrodiol formed. The results demonstrate that both the metabolite pattern and the nucleoside-metabolite complexes formed by the placental microsomes in vitro differed greatly from those produced by rat liver microsomes. These studies also suggest that it is not possible to predict specific patterns of DNA binding from AHH measurements or even from BP metabolite patterns, especially when comparing different tissues and species.     

Comparative carcinogenicity of picene and dibenz[a,h]anthracene in the rat.

Early carcinogenicity tests found no evidence of activity for picene but found considerable initiating and carcinogenic activity for dibenz[a,h]anthracene (DBA). More recent investigation suggested that both pentacyclics were complete carcinogens when administered as single sc injections in NMRI mice, despite findings that picene acted as neither an initiating nor promoting agent. To investigate this contradiction, the complete carcinogenicities of both isomers were compared by sc injection in female Sprague-Dawley rats. The results demonstrate that 1 micromol of DBA, administered three times weekly for 20 doses, induces sarcomas in all test animals by 33 weeks (100%). Similar treatment with picene did not induce sarcoma in any test animals by 37 weeks (0%). The present results agree with the earlier studies. It follows from these results that the predictions of the unified theory for the appearance of carcinogenic properties following administration of picene and dibenz[a,h]anthracene to test animals have been confirmed.     

Formation of DAN-binding products from isolated benzo[a]pyrene metabolites in rat liver nuclei

Liver nuclei from 3-methylcholanthrene-treated rats in the presence of NADPH metabolized 3- and 9-hydroxybenzo[a]pyrene and 7,8-dihydro-7,8-dihydroxybenzo[a]pyrene to products that bound to DNA. Maximal binding was obtained with the dihydrodiol which was approximately 3-fold that with 9-hydroxybenzo[a]pyrene, and 60-fold that with 3-hydroxybenzo[a]pyrene, as substrates. Both 4,5-dihydro-4,5-dihydroxybenzo[a]pyrene and 9,10-dihydro-9,10-dihydroxybenzo[a]pyrene were also extensively metabolized by the nuclear fraction but did not give rise to DNA-binding products.The available evidence suggests that the DNA binding species derived from 9-hydroxy-benzo[a]pyrene is 9-hydroxy-benzo[a]pyrene-4,5-oxide and from 7,8-dihydro-7,8-dihydroxybenzo[a]pyrene, as previously observed in different systems, 7,8-dihydro-7,8-dihydroxy-benzo[a]pyrene-9,10-oxide.     

Glass-capillary-gas chromatography/mass spectrometry data of mono- and polyhydroxylated benz[a]anthracene. Comparison with benz[a]anthracene metabolites from rat liver microsomes

By means of glass-capillary-gas chromatography all possible benz[a]anthracene metabolites formed by rat liver microsomes (phenols, dihydrodiols, dihydrodiol enols and tetrahydrotetrols) can be separated. Mass spectra of their trimethylsilyl ethers show intense molecule ions and, in most cases, characteristic fragments. K-Region diols and their secondary oxidation products can be recognized by the ratio (m/e 147) (m/e 191) greater than 1, whereas the ratio is inverse in all other dihydrodiol trimethylsilyl ethers investigated. With the exception of 1,2-dihydrobenz[a]anthracene-1,2,3-triol all vicinal dihydrodiol enols investigated exhibit an intense elimination of the fragment CH = CH-OSiMe3 according to m/e 379. The conformation of vicinal tetrahydrobenz[a]anthracenetetrols possibly can be distinguished by the intensity of m/e 380 (M - 240) since only in those possessing two or more subsequent Me3SiO groups in the same conformation intense elimination of Me3Si-O-CH = CH-O-SiMe3 is observed. Retention times and mass spectrometric data of a series of synthetic benz[a]anthracene derivatives are presented as a base for the identification of benz[a]anthracene metabolites in biological systems.     

The metabolism of 7,12-dimethylbenz[a]anthracene and 7-hydroxymethyl-12-methylbenz[a]anthracene by rat liver and adrenal homogenates and by rat adrenocortical cells

The metabolism of 3H-labelled 7,12-dimethylbenz[a]anthracene (DMBA) and of 7-hydroxymethyl-12-methylbenz[a]anthracene (7-OHM-12-MBA) into solvent- and water-soluble and protein-bound derivatives has been examined in rat liver and adrenal homogenates and in rat adrenocortical cells in culture. Although the overall extents of metabolism of the substrates by the two types of homogenate were similar, there was twice as much binding to protein in incubations with the 7-hydroxymethyl derivative. Rat adrenal cells in culture metabolized DMBA more extensively than 7-OHM-12-MBA and converted much more of the parent hydrocarbon into water-soluble derivatives. Both hydrocarbons were metabolized to yield dihydrodiols that were separated and identified by high performance liquid chromatography (HPLC). The 8,9-dihydrodiol was the major dihydrodiol formed from DMBA but, with 7-OHM-12-MBA as substrate, metabolism was diverted to the 10,11- and 3,4-positions in adrenal and hepatic preparations respectively. The viability of rat adrenocortical cells in culture, as measured by trypan blue exclusion, did not appear to be affected by treatment with DMBA, 7-OHM-12-MBA, the sulphate ester of 7-OHM-12-MBA or by 3,4-dihydro-3,4-dihydroxy-7-hydroxymethyl-12-methylbenz[a]anthracene.     

Metabolite repression inhibits degradation of benzo[a]pyrene and dibenz[a,h]anthracene by Stenotrophomonas maltophilia VUN 10,003

Large inocula of Stenotrophomonas maltophilia VUN 10,003 were used to investigate bacterial degradation of benzo[a]pyrene and dibenz[a,h]anthracene. Although strain VUN 10,003 was capable of degrading 10–15 mg l⁻¹ of the five-ring compounds in the presence of pyrene after 63 days, further addition of pyrene after degradation of the five-ring polycyclic aromatic hydrocarbons (PAHs) ceased did not stimulate significant decreases in the concentration of benzo[a]pyrene or dibenz[a,h]anthracene. However, pyrene was degraded to undetectable levels 21 days after its addition. The amount of benzo[a]pyrene and dibenz[a,h]anthracene degraded by strain VUN 10,003 was not affected by the initial concentration of the compounds when tested at 25–100 mg l⁻¹, by the accumulation of by-products from pyrene catabolism or a loss of ability by the cells to catabolise benzo[a]pyrene or dibenz[a,h]anthracene. Metabolite or by-product repression was suspected to be responsible for the inhibition: By-products from the degradation of the five-ring compounds inhibited their further degradation. Journal of Industrial Microbiology & Biotechnology (2002) 28, 88–96 DOI: 10.1038/sj/jim/7000216 Received 30 January 2001/ Accepted in revised form 10 October 2001     

Rat liver microsomal metabolites of 7-methylbenz[c]acridine

The metabolism of the weak carcinogen 7-methylbenz[c]acridine (7MBAC) was examined in rat liver microsomes from 3-methylcholanthrene(MC)-induced animals by the use of mixed ¹⁴C- and ²H-labelled substrate. The three metabolites identified by spectroscopic and chromatographic examination were 7-OHMBAC and two dihydrodiols. The dihydrodiols were assigned structures consistent with attack on the 8,9- and 5,6- or K-region of the aromatic system.     

Characteristics of microsomal reduction of benzo[a]pyrene 4,5-oxide

NADPH-reduction of benzo[a]pyrene 4,5-oxide (BP-4,5-oxide) to BP required four components from rat liver: cytochrome P-450, NADPH cytochrome P-450 reductase, phosphatidylcholine and a soluble, heat-sensitive factor which was present in 105 000 × g supernatant and was also released from microsomes by sonication. The requirement for this factor contrasts with recently reported results from Sugiura et al. (Cancer Res., 40 (1980) 2910). Oxide-reduction was 40 times faster under anaerobic conditions, but oxygen did not affect the stimulation factor. This stimulation was highest (× 15) at low concentrations of microsomal protein (<0.1 mg/ml) and was almost absent at high concentrations of microsomal protein (>1 mg/ml). Oxide-reduction activity was proportional to microsomal protein concentration in the presence of added 105 000 × g supernatant, but for microsomes alone (>0.1 mg/ml) exhibited a parallel plot with an intercept at 0.08 mg/ml microsomal protein. Stimulation was highest at high concentrations of BP-4,5-oxide and a linear plot of V⁻¹ vs. [BP-4,5-oxide]⁻¹ was only obtained in the presence of 105 000 × g supernatant (K_m = 3 μM, V_max = 3.3 nmol/mg/min). Microsomal hydration of BP-4,5-oxide (inhibited in reductase assays) was unaffected by 105 000 × g supernatant, suggesting that stimulation of oxide-reduction did not derive from solubilization of BP-4,5-oxide. Stimulation was observed in the initial rate of reaction and was independent of incubation time. Inhibition of lipid peroxidation, removal of peroxides and deoxygenation were all excluded as explanations of the stimulatory effect.     

Epoxy derivatives of aromatic polycyclic hydrocarbons. The synthesis of dibenz[a,c]anthracene 10,11-oxide and its metabolism by rat liver preparations

The synthesis of dibenz[a,c]anthracene 10,11-oxide is described. The oxide was unstable and was rapidly decomposed with cold mineral acid into a mixture of 10- and 11- hydroxydibenz[a,c]anthracene. The oxide was converted by rat liver microsomal preparations and homogenates into a product that is probably 10,11-dihydro-10,11-dihydroxydibenz[a,c]anthracene and which was identical with the metabolite formed when dibenz[a,c]anthracene was metabolized by rat liver homogenates. The oxide did not react either chemically or enzymically with GSH. 10,11-Dihydrodibenz[a,c]anthracene and 10,11-dihydrodibenz[a,c]anthracene 12,13-oxide were both metabolized by rat liver preparations into trans-10,11,12,13-tetrahydro-10,11-dihydroxydibenz[a,c] anthracene and the oxide was converted chemically into this dihydroxy compound, and it reacted chemically but not enzymically with GSH. In the alkylation of 4-(p-nitrobenzyl)pyridine, the ;K-region' epoxide, dibenz[a,h]anthracene 5,6-oxide, was more active than either dibenz[a,c]anthracene 10,11-oxide or 10,11-dihydrobenz[a,c]anthracene 12,13-oxide.     

Photooxidation products of 7,12-dimethylbenz[a]anthracene.

The principal products of the photooxidation of 7,12-dimethylbenz[a]-anthracene (DMBA) in aqueous solutions by photooxidation induced by laboratory lighting have been characterized by high performance liquid chromatograms (HPLC), ultraviolet and mass spectrograms and by comparisons with authentic samples. The products identified were the 7,12-epidioxy-7,12-dihydro-7-12-dimethyl-, 7,12-dione, 7-hydroxymethyl-12-methyl-, 12-hydroxymethyl-7-methyl-, 7-formyl-12-methyl-, 12-formyl-7-methyl-, and 12-hydroxy-12-methyl-7-one derivatives of benz[a]-anthracene. The HPLC profile of products is similar to that obtained from oxidation of DMBA by 'one-electron' reagents, singlet oxygen, or liver microsomal metabolism. The first points of attack are the 7- and 12- positions. The mechanism of photooxidation appears to be generation of singlet oxygen by photodynamic effect of DMBA. None of the products is photosensitizing, however.     

HPLC separation of 32P-postlabelled DNA adducts formed from dibenz[a,h]anthracene in skin.

Mouse skin and human skin have been treated in vivo or in short-term organ culture with dibenz[a,h]anthracene (DB[a,h]A), the related 3,4- or 5,6-diols or the anti- or syn-3,4-diol 1,2-oxides. DNA hydrolysates have been 32P-postlabelled and the adducts present examined by HPLC using a phenyl-modified reverse phase column and, for comparison, by PEI-cellulose TLC and autoradiography. The adducts formed when the diol-epoxides were reacted with salmon sperm DNA were also examined. The results show that in mouse skin treated in vivo, the major adducts formed from DB[a,h]A and the 3,4-diol were the same and that two of them were more polar than those formed in skin or in DNA that had been treated with the related anti- or syn-diol epoxides. Human skin treated with DB[a,h]A in culture yielded an adduct profile that was qualitatively similar to the profiles obtained with mouse skin.     

Microbial metabolism and detoxification of 7,12-dimethylbenz[a]anthracene

Summary Six strains of fungi grown on Sabouraud dextrose broth in the presence of 7,12-dimethylbenz[a]anthracene (DMBA) were surveyed for their ability to metabolize DMBA. Experiments with [¹⁴C]DMBA indicated that the extent of formation of organic-soluble metabolites ranged from 6 to 28% after 5 days of incubation, depending on the organism tested. The yields of water-soluble metabolites also varied, and ranged from 1 to 33% after 5 days.Cunninghamella elegans ATCC 36112 andSyncephalastrum racemosum UT-70 exhibited the highest DMBA-metabolizing activity among the organisms surveyed.S. racemosum metabolized DMBA primarily to 7-hydroxymethyl-12-methylbenz[a]anthracene (7-OHM-12-MBA)_ and 7,12-dihydroxymethylbenz[a]anthracene (7,12-diOHMBA). Minor metabolites included 7-OHM-12-MBA-trans-5,6-, 8,9- and 10,11-dihydrodiols, and glucuronide and sulfate conjugates of phenolic derivatives of DMBA. In contrast, the major DMBA metabolites produced byC. elegans were water-soluble. The predominant organic-soluble metabolites produced byC. elegans included 7-OHM-12-MBA-trans-5,6-, 8,9- and 10,11-dihydrodiols. DMBA-trans-3,4-dihydrodiol was also detected. Circular dichroism spectral analysis revealed that the major enantiomer of the 7-OHM-12-MBA-trans-8,9-dihydrodiol formed by each organism has anS,S absolute configuration, while the major enantiomers of the 5,6-, 10,11- and 3,4-dihydrodiols had anR,R configuration. The mutagenic activity of extracts fromS. racemosum exposed to DMBA were determined inSalmonella typhimurium TA98. The mutagenicity of DMBA decreased by 36% over a period of 5 days as 33% of the compound was metabolized. Comparison of these results with previously reported results in mammalian systems suggests that there are similarities and differences between the fungal and mammalian oxidation of DMBA and that the overall balance of fungal metabolism is towards a detoxification rather than a bioactivation pathway.