Degradation of benzo[a]pyrene by Mycobacterium vanbaalenii PYR-1

Metabolism of the environmental pollutant benzo[a]pyrene in the bacterium Mycobacterium vanbaalenii PYR-1 was examined. This organism initially oxidized benzo[a]pyrene with dioxygenases and monooxygenases at C-4,5, C-9,10, and C-11,12. The metabolites were separated by reversed-phase high-performance liquid chromatography (HPLC) and characterized by UV-visible, mass, nuclear magnetic resonance, and circular dichroism spectral analyses. The major intermediates of benzo[a]pyrene metabolism that had accumulated in the culture media after 96 h of incubation were cis-4,5-dihydro-4,5-dihydroxybenzo[a]pyrene (benzo[a]pyrene cis-4,5-dihydrodiol), cis-11,12-dihydro-11,12-dihydroxybenzo[a]pyrene (benzo[a]pyrene cis-11,12-dihydrodiol), trans-11,12-dihydro-11,12-dihydroxybenzo[a]pyrene (benzo[a]pyrene trans-11,12-dihydrodiol), 10-oxabenzo[def]chrysen-9-one, and hydroxymethoxy and dimethoxy derivatives of benzo[a]pyrene. The ortho-ring fission products 4-formylchrysene-5-carboxylic acid and 4,5-chrysene-dicarboxylic acid and a monocarboxylated chrysene product were formed when replacement culture experiments were conducted with benzo[a]pyrene cis-4,5-dihydrodiol. Chiral stationary-phase HPLC analysis of the dihydrodiols indicated that benzo[a]pyrene cis-4,5-dihydrodiol had 30% 4S,5R and 70% 4R,5S absolute stereochemistry. Benzo[a]pyrene cis-11,12-dihydrodiol adopted an 11S,12R conformation with 100% optical purity. The enantiomeric composition of benzo[a]pyrene trans-11,12-dihydrodiol was an equal mixture of 11S,12S and 11R,12R molecules. The results of this study, in conjunction with those of previously reported studies, extend the pathways proposed for the bacterial metabolism of benzo[a]pyrene. Our study also provides evidence of the stereo- and regioselectivity of the oxygenases that catalyze the metabolism of benzo[a]pyrene in M. vanbaalenii PYR-1.     

The formation of dihydrodiols from benzo[alpha]pyrene by oxidation with an ascorbic acid/ferrous sulphate/EDTA system.

In the oxidation of benzo[alpha]pyrene in an abscorbic acid-ferrous sulphate-EDTA system, four dihydrodiols were detected. Three, trans-4,5-dihydro-4,5-dihydroxybenzo[alpha]pyrene, trans-7,8-dihydro-7,8-dihydroxybenzo[alpha]pyrene and trans-9,10-dihydro-9,10-dihydroxybenzo[alpha]pyrene were identified by their UV spectra and by direct comparisons of their chromatographic properties, using HPLC, with those of the authentic compounds. The fourth compound appeared to be trans-11,12-dihydro-11,12-dihydroxybenzo[alpha]pyrene since its ultraviolet spectrum was identical to that of the cis-dihydrodiol. Time-course experiments showed that the maximum amounts of products were obtained after 8 h of oxidation. A re-examination of the dihydrodiols formed from benzo[alpha]pyrene by rat-liver microsomal fractions failed to show the formation of the trans-11,12-dihydrodiol.     

Metabolic activation of benzo[a]pyrene in human skin maintained in short-term organ culture

The metabolic activation of benzo[a]pyrene (BP) was examined in six samples of human skin after topical application of the hydrocarbon to the skin in short-term organ culture. The results show that all of the samples were capable of metabolizing BP to water-soluble products and to ether-soluble products that included the 4,5-, 7,8- and 9,10-dihydrodiols and a product which had chromatographic properties identical with those of authentic trans-11,12-dihydro-11,12-dihydroxybenzo[a]pyrene (BP-11,12-diol). The major BP-deoxyribonucleoside adduct detected in each skin sample appeared to be formed from the reaction of r-7,t-8-dihydroxy-t-9,10-oxy-7,8,9,10-tetrahydrobenzo[a]pyrene (anti-BP-7,8-diol 9,10-oxide) with deoxyguanosine residues in DNA.     

Formation of DNA-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.     

Dual-label high-performance liquid chromatographic assay for femtomole levels of benzo[a]pyrene metabolites

A dual-label HPLC assay to measure femtomole quantities of ethyl acetate-extractable [3H]benzo[a]pyrene metabolites was developed. 14C-labeled metabolites of benzo[a]pyrene formed by rat liver 9000g supernatant were used as both internal standards and chromatographic markers. The percentage deviation between assays was determined to be between 11 and 13% for 9,10-dihydro-9,10-dihydroxybenzo[a]pyrene, 7,8-dihydro-7,8-dihydroxybenzo[a]pyrene, benzo[a]pyrene-3,6-quinone, benzo[a]pyrene-1,6-quinone, and 9-hydroxybenzo[a]pyrene, 22% for 4,5-dihydro-4,5-dihydroxybenzo[a]pyrene, and less than 5% for 3-hydroxybenzo[a]pyrene. The detection limit of this assay was between 3 and 10 fmol per metabolite. The application of this technique to the metabolism of [3H]benzo[a]pyrene by microsomes of hamster and human oral cavity tissue is described.     

The formation of dihydrodiols by chemical or enzymic oxidation of 3-methylcholanthrene.

The chemical oxidation of 3-methylcholanthrene in an ascorbic acid-ferrous sulphate-EDTA reaction mixture gave all five possible dihydrodiols. The structures and stereochemistry of the dihydrodiols were shown by UV, mass and NMR spectral studies and by chemical examination to be cis-2a,3-dihydroxy-3-methylcholanthrene, trans-4,5-dihydro-4,5-dihydroxy-3-methylcholanthrene, trans-7,8-dihydro-7,8-dihydroxy-3-methylcholanthrene, trans-9,10-dihydro-9,10-dihydroxy-3-methylcholanthrene, cis-11,12-dihydro-11,12-dihydroxy-3-methylcholanthrene and trans-11,12-dihydro-11,12-dihydroxy-3-methylcholanthrene. An examination by HPLC of the dihydrodiols formed in the metabolism of 3-methylcholanthrene by rat-liver microsomal preparations showed the presence of trans-4,5-dihydro-4,5-dihydoxy-3-methylcholanthrene, trans-7,8-dihydro-7,8-dihydroxy-3-methylcholanthrene, trans-9,10-dihydro-9,10-dihydroxy-3-methylcholanthrene and trans-11,12-dihydro-11,12-dihydroxy-3-methylcholanthrene, identified by comparison of their UV and chromatographic characteristics with those of authentic standards. Tentative identification of cis- and trans-1,2-dihydroxy-3-methylcholanthrene, cis-2a,3-dihydroxy-3-methylcholanthrene and cis-11,12-dihydro-11,12-dihydroxy-3-methylcholanthrene as metabolites were made from their mobilities using HPLC. A quantitative comparison of the dihydrodiols formed from 3H-labelled 3-methylcholanthrene by microsomal preparations from the livers of normal and 3-methylcholanthrene-treated rats was carried out. trans-9,10-Dihydro-9,10-dihydroxy-3-methylcholanthrene and cis- and trans-1,2-dihydroxy-3-methylcholanthrene were formed when 3-methylcholanthrene was incubated with mouse skin in organ culture.     

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.     

Identification of the 11,12-dihydro-11,12-dihydroxybenzo(a)pyrene as a major metabolite produced by the green alga, Selenastrum capricornutum

Benzo(a)pyrene metabolites were isolated after incubation of [14C]-benzo(a)pyrene with the green alga, Selenastrum capricornutum. A significant amount of radioactivity chromatographed in the dihydrodiol region which did not coelute with any of the previously identified dihydrodiol metabolites isolated from this system. Following characterization by mass spectrometry, fluorescence spectroscopy, and high pressure liquid chromatography, this metabolite was identified as the cis-11,12-dihydro-11,12-dihydroxybenzo(a)pyrene. This metabolite has not been identified previously as a metabolite formed in a plant system.     

Pyrene degradation by a Mycobacterium sp.: identification of ring oxidation and ring fission products.

The degradation of pyrene, a polycyclic aromatic hydrocarbon containing four aromatic rings, by pure cultures of a Mycobacterium sp. was studied. Over 60% of [14C]pyrene was mineralized to CO2 after 96 h of incubation at 24 degrees C. High-pressure liquid chromatography analyses showed the presence of one major and at least six other metabolites that accounted for 95% of the total organic-extractable 14C-labeled residues. Analyses by UV, infrared, mass, and nuclear magnetic resonance spectrometry and gas chromatography identified both pyrene cis- and trans-4,5-dihydrodiols and pyrenol as initial microbial ring-oxidation products of pyrene. The major metabolite, 4-phenanthroic acid, and 4-hydroxyperinaphthenone and cinnamic and phthalic acids were identified as ring fission products. 18O2 studies showed that the formation of cis- and trans-4,5-dihydrodiols were catalyzed by dioxygenase and monooxygenase enzymes, respectively. This is the first report of the chemical pathway for the microbial catabolism of pyrene.     

Pyrene degradation by a Mycobacterium sp.: identification of ring oxidation and ring fission products

The degradation of pyrene, a polycyclic aromatic hydrocarbon containing four aromatic rings, by pure cultures of a Mycobacterium sp. was studied. Over 60% of [14C]pyrene was mineralized to CO2 after 96 h of incubation at 24 degrees C. High-pressure liquid chromatography analyses showed the presence of one major and at least six other metabolites that accounted for 95% of the total organic-extractable 14C-labeled residues. Analyses by UV, infrared, mass, and nuclear magnetic resonance spectrometry and gas chromatography identified both pyrene cis- and trans-4,5-dihydrodiols and pyrenol as initial microbial ring-oxidation products of pyrene. The major metabolite, 4-phenanthroic acid, and 4-hydroxyperinaphthenone and cinnamic and phthalic acids were identified as ring fission products. 18O2 studies showed that the formation of cis- and trans-4,5-dihydrodiols were catalyzed by dioxygenase and monooxygenase enzymes, respectively. This is the first report of the chemical pathway for the microbial catabolism of pyrene.     

Degradation of Benzo[a]pyrene by Mycobacterium vanbaalenii PYR-1

Metabolism of the environmental pollutant benzo[a]pyrene in the bacterium Mycobacterium vanbaalenii PYR-1 was examined. This organism initially oxidized benzo[a]pyrene with dioxygenases and monooxygenases at C-4,5, C-9,10, and C-11,12. The metabolites were separated by reversed-phase high-performance liquid chromatography (HPLC) and characterized by UV-visible, mass, nuclear magnetic resonance, and circular dichroism spectral analyses. The major intermediates of benzo[a]pyrene metabolism that had accumulated in the culture media after 96 h of incubation were cis-4,5-dihydro-4,5-dihydroxybenzo[a]pyrene (benzo[a]pyrene cis-4,5-dihydrodiol), cis-11,12-dihydro-11,12-dihydroxybenzo[a]pyrene (benzo[a]pyrene cis-11,12-dihydrodiol), trans-11,12-dihydro-11,12-dihydroxybenzo[a]pyrene (benzo[a]pyrene trans-11,12-dihydrodiol), 10-oxabenzo[def]chrysen-9-one, and hydroxymethoxy and dimethoxy derivatives of benzo[a]pyrene. The ortho-ring fission products 4-formylchrysene-5-carboxylic acid and 4,5-chrysene-dicarboxylic acid and a monocarboxylated chrysene product were formed when replacement culture experiments were conducted with benzo[a]pyrene cis-4,5-dihydrodiol. Chiral stationary-phase HPLC analysis of the dihydrodiols indicated that benzo[a]pyrene cis-4,5-dihydrodiol had 30% 4S,5R and 70% 4R,5S absolute stereochemistry. Benzo[a]pyrene cis-11,12-dihydrodiol adopted an 11S,12R conformation with 100% optical purity. The enantiomeric composition of benzo[a]pyrene trans-11,12-dihydrodiol was an equal mixture of 11S,12S and 11R,12R molecules. The results of this study, in conjunction with those of previously reported studies, extend the pathways proposed for the bacterial metabolism of benzo[a]pyrene. Our study also provides evidence of the stereo- and regioselectivity of the oxygenases that catalyze the metabolism of benzo[a]pyrene in M. vanbaalenii PYR-1.     

Effect of purified epoxide hydrolase on metabolic activa-tion and binding of benzo(a)pyrene to exogenous DNA. Shift of the activation pathway

The effect of purified epoxide hydrolase (E.C. 3.3.2.3) on the binding of benzo(a)pyrene metabolites 9-hydroxybenzo(a)pyrene and 7,8-dihydro-7,8-dihydroxybenzo(a)pyrene to DNA catalyzed by cytochrome P 448 from liver microsomes of methylcholanthrene pretreated rats has been investigated. The total binding and the major binding species derived from 9-hydroxybenzo(a)pyrene were strongly inhibited by the presence of purified epoxide hydrolase and the species derived from 7,8-dihydro-7,8-dihydroxybenzo(a)pyrene was slightly increased. By modifying the balance between cytochrome P 448 and epoxide hydrolase it is possible to shift quantitatively the binding of these two main reactive intermediates to DNA.     

Study of biochemical pathways and enzymes involved in pyrene degradation by Mycobacterium sp. strain KMS

Pyrene degradation is known in bacteria. In this study, Mycobacterium sp. strain KMS was used to study the metabolites produced during, and enzymes involved in, pyrene degradation. Several key metabolites, including pyrene-4,5-dione, cis-4,5-pyrene-dihydrodiol, phenanthrene-4,5-dicarboxylic acid, and 4-phenanthroic acid, were identified during pyrene degradation. Pyrene-4,5-dione, which accumulates as an end product in some gram-negative bacterial cultures, was further utilized and degraded by Mycobacterium sp. strain KMS. Enzymes involved in pyrene degradation by Mycobacterium sp. strain KMS were studied, using 2-D gel electrophoresis. The first protein in the catabolic pathway, aromatic-ring-hydroxylating dioxygenase, which oxidizes pyrene to cis-4,5-pyrene-dihydrodiol, was induced with the addition of pyrene and pyrene-4,5-dione to the cultures. The subcomponents of dioxygenase, including the alpha and beta subunits, 4Fe-4S ferredoxin, and the Rieske (2Fe-2S) region, were all induced. Other proteins responsible for further pyrene degradation, such as dihydrodiol dehydrogenase, oxidoreductase, and epoxide hydrolase, were also found to be significantly induced by the presence of pyrene and pyrene-4,5-dione. Several nonpathway-related proteins, including sterol-binding protein and cytochrome P450, were induced. A pyrene degradation pathway for Mycobacterium sp. strain KMS was proposed and confirmed by proteomic study by identifying almost all the enzymes required during the initial steps of pyrene degradation.     

Host-mediated mutagenicity experiments with benzo[a]pyrene and two of its metabolites

Benzo[a]pyrene (BP) and two of its major metabolites, the ultimate mutagen BP-4,5-oxide and the proximate mutagen trans-7,8-dihydro-7,8-dihydroxybenzo[a]pyrene (BP-7,8-diol) were investigated for mutagenicity in Salmonella typhimurium TA1538, TA98 and TA100 using an intrasanguineous host-mediated assay. BP and BP-4,5-oxide were not mutagenic under any experimental conditions. BP-7,8-diol was inactive with the strain TA1538 but was mutagenic with the strains TA98 and TA100. The effect was potentiated by pretreatment of the host mice with the cytochrome P-450 inducer 5,6-benzoflavone. We conclude: (i) one of the reasons for the observed insensitivity of the intrasanguineous host-mediated assay towards BP is that BP-4,5-oxide, which contributes to the microsome-mediated mutagenicity of BP, is inactive in the host-mediated assay; (ii) the finding that BP-7,8-diol is mutagenic in the host-mediated assay demonstrates that the lack of mutagenicity of BP is not intrinsic; (iii) the potentiated mutagenicity after treatment of the hosts with 5,6-benzoflavone suggests that cytochrome P-450 is more important in the activation of BP-7,8-diol in this system than other enzymes (e.g. prostaglandin synthase) that can also activate this compound in vitro.     

Fluorescence study of DNA-complexes formed after metabolic activation of benzo(a)pyrene derivatives

Benzo(a)pyrene derivatives (1-, 2-, 3-, 7-, and 9-hydroxy-benzo(a)pyrene and trans-9,10-dihydro-9,10-dihydroxy-, -4,5-dihydro-4,5-dihydroxy-, and -7,8-dihydro-7,8-dihydroxy-benzo(a)pyrene) were metabolized by liver microsomes isolated from 3-methylcholanthrene-treated rats in the presence of calf thymus DNA. The isolated DNA was then assayed by fluorescence for bound metabolic products. Only 2-hydroxy-benzo(a)pyrene, 9-hydroxy-benzo(a)pyrene and trans-7,8-dihydro-7,8-dihydroxy-benzo(a)pyrene yielded detectable amounts of DNA-bound products. In contrast to the product(s) from 9-hydroxy-benzo(a)pyrene, the metabolites of 2-hydroxy-benzo(a)pyrene and trans-7,8-dihydro-7,8-dihydroxy-benzo(a)pyrene, both strong carcinogens, had similar excitation spectra and gave considerably increased fluorescence intensities when the DNA was denatured. These data indicate structural similarities in the DNA complexes formed after metabolic activation of 2-hydroxy-benzo(a)pyrene and trans-7,8-dihydro-7,8-dihydroxy-benzo(a)pyrene.     

Chemical rearrangement of phenol-epoxide metabolites of polycyclic aromatic hydrocarbons to quinone-methides

Evidence of the involvement of triol-epoxide and phenol-epoxide metabolites in the metabolic activation of polycyclic hydrocarbons is accumulating. It is proposed that the phenolic OH-groups present in such epoxides will activate the epoxide moieties and permit their rearrangement to quinone-methides. These quinone-methides are highly reactive, potentially-isolable chemical entities with strong alkylating activity. In one resonance form they are resonance-stabilized carbonium ions. Only epoxides that also possess phenolic OH-groups in certain positions will form quinone-methides: these appear to include 9-hydroxybenzo [a] pyrene 4,5-oxide and the triol-epoxides 9-hydroxy-trans-1,2-dihydro-1,2-dihydroxychrysene 3,4-oxide and 2-hydroxy-trans-9,10-dihydro-9,10-dihydroxybenzo[a]pyrene 7,8-oxide.     

Prostaglandin synthetase dependent activation of 7,8-dihydro-7,8-dihydroxy-geno (a) pyrene to mutagenic derivativies.

The combination of arachidonic acid and a Tween 20 solubilized enzyme preparation from sheep seminal vesicles converts 7,8-dihydro-7,8-dihydroxy-benzo(a)pyrene to derivatives strongly mutagenic to $\text{Salmonella typhimurium}$ tester strain TA 98. Under similar conditions no activation of benzo(a)pyrene, 4,5-dihydro-4,5-dihydroxy-benzo(a)pyrene, or 9,10-dihydro-9,10-dihydroxy-benzo(a)pyrene occurs. The activation of 7,8-dihydro-7,8-dihydroxy-benzo(a)-pyrene is markedly reduced by the omission of arachidonic acid and is inhibited by the prostaglandin synthetase inhibitor indomethacin. 100 μM butylated hydroxyanisole is also an effective inhibitor. This is the first report of the metabolic activation of 7,8-dihydro-7,8-dihydroxy-benzo(a)pyrene by an enzyme system distinct from the mixed-function oxidases.     

Heme-dependent rubber oxygenase RoxA of Xanthomonas sp. cleaves the carbon backbone of poly(cis-1,4-Isoprene) by a dioxygenase mechanism

Oxidative cleavage of poly(cis-1,4-isoprene) by rubber oxygenase RoxA purified from Xanthomonas sp. was investigated in the presence of different combinations of (16)O(2), (18)O(2), H(2)(16)O, and H(2)(18)O. 12-oxo-4,8-dimethyl-trideca-4,8-diene-1-al (ODTD; m/z 236) was the main cleavage product in the absence of (18)O-compounds. Incorporation of one (18)O atom in ODTD was found if the cleavage reaction was performed in the presence of (18)O(2) and H(2)(16)O. Incubation of poly(cis-1,4-isoprene) (with RoxA) or of isolated unlabeled ODTD (without RoxA) with H(2)(18)O in the presence of (16)O(2) indicated that the carbonyl oxygen atoms of ODTD significantly exchanged with oxygen atoms derived from water. The isotope exchange was avoided by simultaneous enzymatic reduction of both carbonyl functions of ODTD to the corresponding dialcohol (12-hydroxy-4,8-dimethyl-trideca-4,8-diene-1-ol (HDTD; m/z 240) during RoxA-mediated in vitro cleavage of poly(cis-1,4-isoprene). In the presence of (18)O(2), H(2)(16)O, and alcohol dehydrogenase/NADH, incorporation of two atoms of (18)O into the reduced metabolite HDTD was found (m/z 244), revealing that RoxA cleaves rubber by a dioxygenase mechanism. Based on the labeling results and the presence of two hemes in RoxA, a model of the enzymatic cleavage mechanism of poly(cis-1,4-isoprene) is proposed.     

Formation of the 11,12-diol as a metabolite of benzo(a)pyrene by rat skin in vivo

The dihydrodiols present as metabolites in rat skin after topical application of ³H-labelled benzo(a)pyrene included a significant amount of radioactivity that cochromatographed with synthetic $\text{trans}$-11,12-dihydro-11,12-dihydroxybenzo(a)pyrene. Treatment of the radioactive metabolite with hot mineral acid gave a product that had chromatographic properties identical to those of the phenol similarly formed from the synthetic dihydrodiol and acetylation of the metabolite yielded a product that cochromatographed with the diacetate of the synthetic dihydrodiol. These observations show that the 11,12-dihydrodiol is formed as a metabolite of BP in rat skin $\text{in vivo}$. The metabolite was not detected in mouse skin.     

Conjugation of benzo[a]pyrene metabolites by freshwater green alga Selenastrum capricornutum

Benzo[a]pyrene (BaP) undergoes metabolic transformation in mammals via oxidative, hydrolytic, and conjugative processes; however, little is known concerning BaP conjugation in freshwater algae. It has been shown in this laboratory that BaP is metabolized by Selenastrum capricornutum via a dioxygenase pathway. This study describes the conjugation of BaP metabolites by a green alga, Selenastrum capricornutum. Cultures were exposed to 1160 micrograms/l [14C]BaP for 4 days at 23 degrees C under gold fluorescent lights on a diurnal cycle of 16 h light, 8 h dark. Of the total metabolites in the algal culture, 89% were present in media. BaP and non-conjugated metabolites were separated from conjugated metabolites by chromatography on neutral alumina columns using solvents of increasing polarity. Seventy-one percent of the BaP metabolites were conjugates of which 12.2%, 12.0% and 12.4% were sulfate ester and alpha- and beta-glucose conjugates, respectively. Conjugates that coeluted with sulfate esters were hydrolyzed with arylsulfatase, alpha- or beta-glucosidase; high performance liquid chromatography (HPLC) analysis indicated that the major product of each enzymatic hydrolysis was the 4,5-dihydrodiol (87.2, 69 and 53%, respectively). Eighty-six percent of the conjugates were acid labile following incubation for 2 h in 4 N HCl at 37 degrees C. To our knowledge this is the first demonstration of the metabolism of a polynuclear aromatic hydrocarbon by a freshwater green alga through a dioxygenase pathway and subsequent conjugation and excretion.