Metabolic activation of polycyclic aromatic hydrocarbon trans-dihydrodiols by ubiquitously expressed aldehyde reductase (AKR1A1)

Polycyclic aromatic hydrocarbons (PAHs) are metabolized to trans-dihydrodiol proximate carcinogens by CYP1A1 and epoxide hydrolase (EH). CYP1A1 or aldo-keto reductases (AKRs) from the 1C subfamily can further activate the trans-dihydrodiols by forming either anti-diol-epoxides or reactive and redox active o-quinones, respectively. To determine whether other AKR superfamily members can divert trans-dihydrodiols to o-quinones, the cDNA encoding human aldehyde reductase (AKR1A1) was isolated from hepatoma HepG2 cells using RT-PCR, subcloned into a prokaryotic expression vector, overexpressed in E. coli and purified to homogeneity in milligram amounts. Studies revealed that AKR1A1 preferentially oxidized the metabolically relevant (-)-[3R,4R]-dihydroxy-3,4-dihydrobenz[a]anthracene. AKR1A1 also displayed high utilization ratios (V(max)/K(m)) for the following PAH trans-dihydrodiols: (+/-)trans-3,4-dihydroxy-3,4-dihydro-7-methylbenz[a]anthracene, (+/-)trans-3,4-dihydroxy-3,4-dihydro-7,12-dimethylbenz[a]anthracene and (+/-)trans-7,8-dihydroxy-7,8-dihydro-5-methylchrysene. Multiple tissue expression (MTE) arrays were used to measure the co-expressed of CYP1A1, EH and AKR1A1. All the three enzymes co-expressed to sites of PAH activation. The high catalytic efficiency of AKR1A1 for potent proximate carcinogen trans-dihydrodiols and its presence in tissues that contain CYP1A1 and EH suggests that it plays an important role in this alternative pathway of PAH activation (supported by CA39504).     

The formation of dihydrodiols by the chemical or enzymic oxidation of benz[a] anthracene and 7,12-dimethylbenz[a] anthracene.

When benz[a] anthracene was oxidised in a reaction mixture containing ascorbic acid, ferrous sulphate and EDTA, the non-K-region dihydrodiols, trans-1,2-dihydro-1,2-dihydroxybenz[a] anthracene and trans-3,4-dihydro-3,4-dihydroxybenz[a] anthracene together with small amounts of the 8,9- and 10,11-dihydrodiols were formed. When oxidised in a similar system, 7,12-dimethylbenz[a] anthracene yielded the K-region dihydrodiol, trans-5,6-dihydro-5,6-dihydroxy-7,12-dimethylbenz[a] anthracene and the non-K-region dihydrodiols, trans-3,4-dihydro-3,4-dihydroxy-7,12-dimethylbenz[a] anthracene, trans-8,9-dihydro-8,9-dihydroxy-7,12-dimethylbenz[a] anthracene, trans-10,11-dihydro-10,11-dihydroxy-7,12-dimethylbenz[a] anthracene and a trace of the 1,2-dihydrodiol. The structures and sterochemistry of the dihydrodiols were established by comparisons of their UV spectra and chromatographic characteristics using HPLC with those of authentic compounds or, when no authentic compounds were available, by UV, NMR and mass spectral analysis. An examination by HPLC of the dihydrodiols formed in the metabolism, by rat-liver microsomal fractions, of benz[a] anthracene and 7,12-dimethylbenz[a] anthracene was carried out. The metabolic dihydriols were identified by comparisons of their chromatographic and UV or fluorescence spectral characteristics with compounds of known structures. The principle metabolic dihydriols formed from both benz[a] anthracene and 7,12-dimethylbenz[a] anthracene were the trans-5,6- and trans-8,9-dihydrodiols. The 1,2- and 10,11-dihydrodiols were identified as minor products of the metabolism of benz [a] anthracene and the tentative identification of the trans-3,4-dihydriol as a metabolite was made from fluorescence and chromatographic data. The minor metabolic dihydriols formed from 7,12-dimethylbenz[a] anthracene were the trans-3,4-dihydrodiol and the trans-10,11-dihydriol but the trans-1,2-dihydrodiol was not detected in the present study.     

Regio- and Stereoselective Metabolism of 7,12-Dimethylbenz[a]anthracene by Mycobacterium vanbaalenii PYR-1

The degradation of 7,12-dimethylbenz[a]anthracene (DMBA), a carcinogenic polycyclic aromatic hydrocarbon, by cultures of Mycobacterium vanbaalenii PYR-1 was studied. When M. vanbaalenii PYR-1 was grown in the presence of DMBA for 136 h, high-pressure liquid chromatography (HPLC) analysis showed the presence of four ethyl acetate-extractable compounds and unutilized substrate. Characterization of the metabolites by mass and nuclear magnetic resonance spectrometry indicated initial attack at the C-5 and C-6 positions and on the methyl group attached to C-7 of DMBA. The metabolites were identified as cis-5,6-dihydro-5,6-dihydroxy-7,12-dimethylbenz[a]anthracene (DMBA cis-5,6-dihydrodiol), trans-5,6-dihydro-5,6-dihydroxy-7,12-dimethylbenz[a]anthracene (DMBA trans-5,6-dihydrodiol), and 7-hydroxymethyl-12-methylbenz[a]anthracene, suggesting dioxygenation and monooxygenation reactions. Chiral stationary-phase HPLC analysis of the dihydrodiols showed that DMBA cis-5,6-dihydrodiol had 95% 5S,6R and 5% 5R,6S absolute stereochemistry. On the other hand, the DMBA trans-5,6-dihydrodiol was a 100% 5S,6S enantiomer. A minor photooxidation product, 7,12-epidioxy-7,12-dimethylbenz[a]anthracene, was also formed. The results demonstrate that M. vanbaalenii PYR-1 is highly regio- and stereoselective in the degradation of DMBA.     

The metabolic activation of 7-methylbenz(a)anthracene in mouse skin

The metabolism of 7-methylbenz(a)anthracene by rat-liver preparations and by mouse skin has been studied using a combination of thin-layer and high pressure liquid chromatography and all five possible trans-dihydrodiols have been detected as metabolites but in different proportions. The roles of these dihydrodiols and of the related vicinal diol-epoxides in the metabolic activation of 7-methylbenz(a)anthracene in mouse skin has been studied using Sephadex LH-20 column chromatography. The results show that the hydrocarbon-nucleic acid products formed in mouse skin in vivo most probably arise from 3,4-dihydro-3,4-dihydroxy-7-methylbenz(a)anthracene 1,2-oxide which, on the basis of this and other evidence, appears to be the reactive intermediate involved in the metabolic activation of 7-methylbenz(a)anthracene in this tissue.     

The metabolism of 7- and 12-methylbenz[a]-anthracene and their derivatives

1. 7- and 12-Methylbenz[a]anthracene were converted by rat-liver homogenates into the corresponding hydroxymethyl derivatives, products that are probably the 8,9-dihydro-8,9-dihydroxy and the 5,6-dihydro-5,6-dihydroxy derivatives, and a number of phenolic products. 2. Both hydrocarbons were converted into glutathione conjugates; that from 7-methylbenz[a]anthracene was also formed, together with 5,6-dihydro-5,6-dihydroxy- and 5-hydroxy-benz[a]anthracene, from 5,6-epoxy-5,6-dihydro-7-methylbenz[a]anthracene. 3. 7- and 12-Hydroxymethyl-benz[a]anthracene were converted into products that are probably 8,9-dihydro-8,9-dihydroxy derivatives, and into phenols. 4. The preparation of a number of derivatives of the hydrocarbons is described. 5. The oxidation of the hydrocarbons with lead tetra-acetate was investigated.     

Purification and Characterization of an Arene cis-Dihydrodiol Dehydrogenase Endowed with Broad Substrate Specificity toward Polycyclic Aromatic Hydrocarbon Dihydrodiols

Initial reactions involved in the bacterial degradation of polycyclic aromatic hydrocarbons (PAHs) include a ring-dihydroxylation catalyzed by a dioxygenase and a subsequent oxidation of the dihydrodiol products by a dehydrogenase. In this study, the dihydrodiol dehydrogenase from the PAH-degrading Sphingomonas strain CHY-1 has been characterized. The bphB gene encoding PAH dihydrodiol dehydrogenase (PDDH) was cloned and overexpressed as a His-tagged protein. The recombinant protein was purified as a homotetramer with an apparent M_r of 110,000. PDDH oxidized the cis-dihydrodiols derived from biphenyl and eight polycyclic hydrocarbons, including chrysene, benz[a]anthracene, and benzo[a]pyene, to corresponding catechols. Remarkably, the enzyme oxidized pyrene 4,5-dihydrodiol, whereas pyrene is not metabolized by strain CHY-1. The PAH catechols produced by PDDH rapidly auto-oxidized in air but were regenerated upon reaction of the o-quinones formed with NADH. Kinetic analyses performed under anoxic conditions revealed that the enzyme efficiently utilized two- to four-ring dihydrodiols, with K_m values in the range of 1.4 to 7.1 μM, and exhibited a much higher Michaelis constant for NAD⁺ (K_m of 160 μM). At pH 7.0, the specificity constant ranged from (1.3 ± 0.1) × 10⁶ M⁻¹ s⁻¹ with benz[a]anthracene 1,2-dihydrodiol to (20.0 ± 0.8) × 10⁶ M⁻¹ s⁻¹ with naphthalene 1,2-dihydrodiol. The catalytic activity of the enzyme was 13-fold higher at pH 9.5. PDDH was subjected to inhibition by NADH and by 3,4-dihydroxyphenanthrene, and the inhibition patterns suggested that the mechanism of the reaction was ordered Bi Bi. The regulation of PDDH activity appears as a means to prevent the accumulation of PAH catechols in bacterial cells.     

The ubiquitous aldehyde reductase (AKR1A1) oxidizes proximate carcinogen trans-dihydrodiols to o-quinones: potential role in polycyclic aromatic hydrocarbon activation

Polycyclic aromatic hydrocarbons (PAHs) are metabolized to trans-dihydrodiol proximate carcinogens by human epoxide hydrolase (EH) and CYP1A1. Human dihydrodiol dehydrogenase isoforms (AKR1C1-AKR1C4), members of the aldo-keto reductase (AKR) superfamily, activate trans-dihydrodiols by converting them to reactive and redox-active o-quinones. We now show that the constitutively and widely expressed human AKR, aldehyde reductase (AKR1A1), will oxidize potent proximate carcinogen trans-dihydrodiols to their corresponding o-quinones. cDNA encoding AKR1A1 was isolated from HepG2 cells, overexpressed in Escherichia coli, purified to homogeneity, and characterized. AKR1A1 oxidized the potent proximate carcinogen (+/-)-trans-7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene with a higher utilization ratio (V(max)/K(m)) than any other human AKR. AKR1A1 also displayed a high V(max)/K(m) for the oxidation of 5-methylchrysene-7,8-diol, benz[a]anthracene-3,4-diol, 7-methylbenz[a]anthracene-3,4-diol, and 7,12-dimethylbenz[a]anthracene-3,4-diol. AKR1A1 displayed rigid regioselectivity by preferentially oxidizing non-K-region trans-dihydrodiols. The enzyme was stereoselective and oxidized 50% of each racemic PAH trans-dihydrodiol tested. The absolute stereochemistries of the reactions were assigned by circular dichroism spectrometry. AKR1A1 preferentially oxidized the metabolically relevant (-)-benzo[a]pyrene-7(R),8(R)-dihydrodiol. AKR1A1 also preferred (-)-benz[a]anthracene-3(R),4(R)-dihydrodiol, (+)-7-methylbenz[a]anthracene-3(S),4(S)-dihydrodiol, and (-)-7,12-dimethylbenz[a]anthracene-3(R),4(R)-dihydrodiol. The product of the AKR1A1-catalyzed oxidation of (+/-)-trans-7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene was trapped with 2-mercaptoethanol and characterized as a thioether conjugate of benzo[a]pyrene-7,8-dione by LC/MS. Multiple human tissue expression array analysis showed coexpression of AKR1A1, CYP1A1, and EH, indicating that trans-dihydrodiol substrates are formed in the same tissues in which AKR1A1 is expressed. The ability of this general metabolic enzyme to divert trans-dihydrodiols to o-quinones suggests that this pathway of PAH activation may be widespread in human tissues.     

High microsome-mediated mutagenicity of the 3,4-dihydrodiol of 7-methylbenz[a]anthracene in S. typhimurium TA 98.

7-Methylbenz[a]anthracene and the 1,2-, 3,4-, 5,6- and 8,9-dihydrodiols derived from this hydrocarbon have been tested for mutagenicity towards S. typhimurium TA 98 in the presence of rat-liver post-mitochondrial supernatant. At non-toxic concentrations, the mutagenicity of the non-K-region 3,4-dihydrodiol was more than ten-fold higher than that of the other K-region and non-K-region dihydrodiols and more than three-fold higher than that of the parent hydrocarbon. 1,1,1-Trichloropropene 2,3-oxide, an inhibitor of epoxide hydratase, increased the microsome-mediated mutagenicity of 7-methylbenz[a]anthracene but did not alter that of the four related dihydrodiols.     

A rapid and reproducible assay for collagenase using [1-14C]acetylated collagen.

A rapid, continuous, and highly sensitive fluorescence assay is described for the measurement of epoxide hydrase activity. The method is based on the large differences between the fluorescence spectra of certain K-region arene oxides and their corresponding trans-dihydrodiols. Enzymatic hydration of K-region arene oxides of phenanthrene, pyrene, benzo[a]pyrene, and 7,12-dimethylbenzo[a]anthracene was studied. The assay was most sensitive with benzo[a]pyrene-4,5-oxide as substrate. With 10 μm benzo[a]pyrene-4,5-oxide, enzymatic rates of 30 pmol of dihydrodiol/min/mg of protein are three to five times those of the blank without enzyme. The fluorometric method described has been used to study site-directed inhibitors of epoxide hydrase and the stereoselective hydration of racemic arene oxides.     

Discovery of potent and selective histamine H3 receptor inverse agonists based on the 3,4-dihydro-2H-pyrazino[1,2-a]indol-1-one scaffold

A novel series of potent histamine H₃ receptor inverse agonists based on the 3,4-dihydro-2H-pyrazino[1,2-a]indol-1-one scaffold has been discovered. Several compounds display high selectivity over other histamine receptor subtypes and have favorable physicochemical properties, low potential for CYP450 enzyme inhibition and high metabolic stability in microsomal preparations. (R)-2-Cyclopropylmethyl-8-(1-isopropyl-piperidin-4-yloxy)-3-methyl-3,4-dihydro-2H-pyrazino[1,2-a]indol-1-one (8t) showed good in vivo efficacy after per os application in an acute rat dipsogenia model of water intake.     

The metabolism of a series of polycyclic hydrocarbons by mouse skin maintained in short-term organ culture

Investigations on the metabolism of ³H-labelled chrysene, benz[a]anthracene, 7-methylbenz[a]anthracene, 7,12-dimethylbenz[a]anthracene, 3-methylcholanthrene, benzo[a]pyrene, dibenz[a,c]anthracene and dibenz[a,h]anthracene by mouse skin maintained in short-term organ culture were carried out. Estimations of the distribution of the metabolites of each hydrocarbon present after 24 h showed that there were wide variations both in the rates at which the hydrocarbons were metabolised and in the amounts of metabolites covalently bound to skin macromolecules. All the hydrocarbons were metabolised to dihydrodiols, which were identified by comparison on high pressure liquid chromatography (HPLC) with the authentic compounds, and these were the same diols as those that were formed in previous experiments with rat-liver microsomal fractions. However, free dihydrodiols represented only relatively small proportions of the total amounts of metabolites formed. All the hydrocarbons yielded dihydrodiols of the type that could give rise to bay-region diol-epoxides, when further metabolised, some of which are thought to be involved in hydrocarbon carcinogenesis.     

Aryl Hydrocarbon Receptor Facilitates DNA Strand Breaks and 8-Oxo-2��-deoxyguanosine Formation by the Aldo-Keto Reductase Product Benzo[a]pyrene-7,8-dione

Polycyclic aromatic hydrocarbon (PAH) o-quinones produced by aldo-keto reductases are ligands for the aryl hydrocarbon receptor (AhR) (Burczynski, M. E., and Penning, T. M. (2000) Cancer Res. 60, 908–915). They induce oxidative DNA lesions (reactive oxygen species-mediated DNA strand breaks and 8-oxo-7,8-dihydro-2′-deoxyguanosine (8-oxo-dGuo) formation) in human lung cells. We tested whether the AhR enhances PAH o-quinone-mediated oxidative DNA damage by translocating these ligands to the nucleus. Using the single cell gel electrophoresis (comet) assay to detect DNA strand breaks in murine hepatoma Hepa1c1c7 cells and its AhR- and aryl hydrocarbon receptor nuclear translocator-deficient variants, benzo[a]pyrene-7,8-dione (B[a]P-7,8-dione) produced fewer DNA strand breaks in AhR-deficient cells compared with aryl hydrocarbon receptor nuclear translocator-deficient and wild type Hepa1c1c7 cells. Decreased DNA strand breaks were also observed in human bronchoalveolar H358 cells in which the AhR was silenced by siRNA. The antioxidant α-tocopherol and the iron chelator/antioxidant desferal decreased the formation of B[a]P-7,8-dione-mediated DNA strand breaks indicating that they were reactive oxygen species-dependent. By coupling the comet assay to 8-oxoguanine glycosylase (hOGG1), which excises 8-oxo-Gua, strand breaks dependent upon this lesion were measured. hOGG1 treatment produced more DNA single strand breaks in B[a]P-7,8-dione-treated Hepa cells and H358 cells than in its absence. The levels of hOGG1-dependent DNA strand breaks mediated by B[a]P-7,8-dione were lower in AhR-deficient Hepa and AhR knockdown H358 cells. The AhR antagonist α-naphthoflavone also attenuated B[a]P-7,8-dione-mediated DNA strand breaks. The decrease in 8-oxo-dGuo levels in AhR-deficient Hepa cells and AhR knockdown H358 cells was validated by immunoaffinity capture stable isotope dilution ([¹⁵N₅]8-oxo-dGuo) liquid chromatography-electrospray ionization/multiple reaction monitoring/mass spectrometry. We conclude that the AhR shuttles PAH o-quinone genotoxins to the nucleus and enhances oxidative DNA damage.Polycyclic aromatic hydrocarbons (PAHs)² are ubiquitous environmental pollutants that include over 200 compounds with two or more fused benzene rings. PAHs are formed as a result of incomplete combustion of fossil fuels (e.g. coal and oil) and are present in car and diesel exhaust and smoked or charbroiled food (1–3). They are also found in cigarette smoke condensate and tobacco products and are suspect agents in the causation of human lung cancer (4, 5). PAHs must be metabolically activated to reactive genotoxins to cause their mutagenic and carcinogenic effects.Two major metabolic activation pathways are possible starting from the proximate PAH carcinogen (−)B[a]P-7,8-trans-dihydrodiol (Fig. 1). The P4501A1/1B1 pathway converts (−)B[a]P-7,8-trans-dihydrodiol to yield (+)-anti-7,8-dihydroxy-9α,10β-epoxy-7,8,9,10-tetrahydroB[a]P (6–8). This diol epoxide forms stable N²-2′-deoxyguanosine (dGuo) adducts in vitro and in vivo (9, 10) and leads to mutation in H-ras (11) and may account for mutations in “hot spots” in p53 observed in lung cancer (12). The G to T transversions most often observed in these genes might arise because of the action of one or more trans-lesional by-pass DNA polymerases that read through stable diol-epoxide DNA adducts with low processivity and fidelity (13, 14).Open in a separate windowFIGURE 1.PAH activation by AKRs to cause oxidative DNA damage.As an alternative, human aldo-keto reductases (AKR1A1 and AKR1C1-AKR1C4) catalyze the NADP⁺-dependent oxidation of (±)B[a]P-7,8-trans-dihydrodiol to produce the electrophilic and redox-active B[a]P-7,8-dione (15, 16). In this pathway, AKRs convert B[a]P-7,8-trans-dihydrodiol to form a ketol that rearranges to a catechol. The catechol then undergoes two subsequent one-electron oxidations to yield the fully oxidized o-quinone. Once formed, B[a]P-7,8-dione amplifies reactive oxygen species (ROS) by entering futile redox cycles that deplete cellular reducing equivalents (e.g. NADPH) (17). PAH o-quinones can undergo 1,4- or 1,6-Michael addition with guanine and adenine bases to form stable N²-dGuo and N⁶-dAdo adducts in vitro (18–20). They can also react with the N7 position of guanine to yield depurinating adducts (21). It is possible that these covalent PAH o-quinone adducts could give to G to T transversion mutations.PAH o-quinones also cause oxidative DNA damage in vitro and in vivo (22–25). Nanomolar concentrations of PAH o-quinones under redox cycling conditions (NADPH and Cu(II)) lead to significant 8-oxo-dGuo formation in bulk DNA, and the responsible oxidant was found to be singlet oxygen (¹O₂) (24, 26). Under these conditions, PAH o-quinones produced 8-oxo-dGuo as the most dominant lesion among the three types of oxidative lesions measured (abasic sites, 8-oxo-dGuo, and oxidized pyrimidines) (26). In a yeast reporter gene assay, which scored loss-of-function mutations in p53, PAH o-quinones were found to be highly mutagenic but only under redox cycling conditions. The dominant mutation observed was a G to T transversion that was suppressed by ROS scavengers (27). Subsequent HPLC analysis coupled with electrochemical detection showed that there was a linear correlation between 8-oxo-dGuo formation in p53 and mutation frequency, indicating that 8-oxo-dGuo was the likely adduct responsible for the G to T transversions observed (28). These data suggest that oxidative DNA lesions caused by PAH o-quinones are more relevant in causing mutation than covalent PAH o-quinone-DNA adducts. In the latter case even if these adducts form, they do not appear to be mutagenic on p53.Recently, using either a hOGG1-coupled comet assay or an immunoaffinity capture-stable isotope dilution liquid chromatography/electrospray ionization/multiple reaction monitoring/mass spectrometry (LC/ESI/MRM/MS) assay, it was shown that both the AKR substrate (B[a]P-7,8-trans-dihydrodiol) and the AKR product (B[a]P-7,8-dione) caused significant DNA strand breaks and 8-oxo-dGuo formation in human lung adenocarcinoma A549 cells (25). Similar results were not observed with (+)-anti-7,8-dihydroxy-9α,10β-epoxy-7,8,9,10-tetrahydroB[a]P or the regioisomer B[a]P-4,5-trans- dihydrodiol in these AKR-expressing cells. Subsequent use of the fluorescent dye dichlorofluorescein diacetate revealed that B[a]P-7,8-dione generated ROS in the nuclear compartment of the cells, suggesting that the PAH o-quinone was transported into the nucleus to increase the ROS-mediated DNA strand breaks and 8-oxo-dGuo (25). In addition, earlier disposition studies detected significant amounts of [³H]B[a]P-7,8-dione in the cell pellets of primary rat hepatocytes within 0.5 h, which caused extensive strand scission of the genomic DNA (29), suggesting that B[a]P-7,8-dione reached the nucleus. However, how PAH o-quinones gain entry into the nucleus and induce oxidative DNA damage is currently unknown.PAH o-quinones are ligands for the aryl hydrocarbon receptor (AhR) (30). These quinones can promote translocation of AhR to nucleus to induce P4501A1 expression. Upon binding with PAH o-quinones, the AhR dissociates from heat shock protein 90 and is rapidly translocated into nucleus where it dimerizes with the aryl hydrocarbon receptor nuclear translocator (ARNT) (31, 32). The quinone-bound AhR·ARNT complex then binds to the xenobiotic response element (XRE) and robustly activates the expression of AhR-regulated genes (30). These data raise the possibility that oxidative DNA damage caused by PAH o-quinones occurs because of their transportation and concentration in the nucleus mediated by the AhR. However, this hypothesis has not been formally tested.We now show that B[a]P-7,8-dione produces AhR-dependent DNA strand breaks and 8-oxo-dGuo formation using murine Hepa1c1c7 cells but not in its AhR-deficient variant. Similar results were obtained in human bronchoalveolar carcinoma H358 cells, but these effects were attenuated when the AhR was knocked down with siRNA. DNA lesions were measured by using the comet assay, which was coupled with hOGG1. These results were also confirmed by LC-ESI/MRM/MS assay for 8-oxo-dGuo. Our finding shows that PAH o-quinones produced by AKRs can cause ROS-mediated genotoxicity via an AhR-dependent mechanism, and this might contribute to PAH-mediated carcinogenesis.     

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.     

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.     

Epoxy derivatives of aromatic polycyclic hydrocarbons. The preparation of benz[a]anthracene 8,9-oxide and 10,11-dihydrobenz[a]anthracene 8,9-oxide and their metabolism by rat liver preparations

The syntheses of 10,11-dihydrobenz[a]anthracene 8,9-oxide, benz[a]anthracene 8,9-oxide and 9-hydroxybenz[a]anthracene are described, together with those of a number of related compounds. The epoxides react both chemically and enzymically with water to yield the corresponding dihydrodiols and with reduced glutathione to form glutathione conjugates, and they react chemically with N-acetylcysteine to yield the corresponding mercapturic acids. 8,9-Dihydro-8,9-dihydroxybenz[a]anthracene, formed enzymically from benz[a]anthracene 8,9-oxide, was identical with a dihydrodiol formed when benz[a]anthracene was metabolized by rat liver homogenates. Similarly 10,11-dihydrobenz[a]anthracene 8,9-oxide yielded a dihydrodiol identical with the product formed when 10,11-dihydrobenz[a]anthracene was metabolized.     

The role of base excision repair genes OGG1, APN1 and APN2 in benzo[a]pyrene-7,8-dione induced p53 mutagenesis

Lung cancer is primarily caused by exposure to tobacco smoke. Tobacco smoke contains numerous carcinogens, including polycyclic aromatic hydrocarbons (PAH). The most common PAH studied is benzo[a]pyrene (B[a]P). B[a]P is metabolically activated through multiple routes, one of which is catalyzed by aldo-keto reductase (AKR) to B[a]P-7,8-dione (BPQ). BPQ undergoes a futile redox cycle in the presence of NADPH to generate reactive oxygen species (ROS). ROS, in turn, damages DNA. Studies with a yeast p53 mutagenesis system found that the generation of ROS by PAH o-quinones may contribute to lung carcinogenesis because of similarities between the patterns (types of mutations) and spectra (location of mutations) and those seen in lung cancer. The patterns were dominated by G to T transversions, and the spectra in the experimental system have mutations at lung cancer hotspots. To address repair mechanisms that are responsible for BPQ induced damage we observed the effect of mutating two DNA repair genes OGG1 and APE1 (APN1 in yeast) and tested them in a yeast reporter system for p53 mutagenesis. There was an increase in both the mutant frequency and the number of G:C/T:A transversions in p53 treated with BPQ in ogg1 yeast but not in apn1 yeast. Knocking out APN2 increased mutagenesis in the apn1 cells. In addition, we did not find a strand bias on p53 treated with BPQ in ogg1 yeast. These studies suggest that Ogg1 is involved in repairing the oxidative damage caused by BPQ, Apn1 and Apn2 have redundant functions and that the stand bias seen in lung cancer may not be due to impaired repair of oxidative lesions.     

Efficient resolution of the dihydrodiol derivatives of benzo[a]pyrene by high-pressure liquid chromatography of the related (−)-dimenthoxyacetates

The diastereomeric (−)-dimenthoxyacetate derivatives of (±)-trans-7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene were efficiently resolved by high-pressure liquid chromatography (HPLC) on silica gel. Treatment with methanolic ammonia under mild conditions removed the menthoxyacetate groups to furnish the optically pure (+) and (−) enantiomers of the trans-dihydrodiol. Epoxidation of each of the latter with m-chloroperbenzoic acid gave the corresponding (−) and (+) anti-diolepoxides. The speed and efficiency of resolution of these relatively sensitive compounds by HPLC demonstrates the potential utility of this technique for resolution of all types of carcinogen-derived arene dihydrodiols.     

Benz[a]anthracene Biotransformation and Production of Ring Fission Products by Sphingobium sp. Strain KK22

A soil bacterium, designated strain KK22, was isolated from a phenanthrene enrichment culture of a bacterial consortium that grew on diesel fuel, and it was found to biotransform the persistent environmental pollutant and high-molecular-weight polycyclic aromatic hydrocarbon (PAH) benz[a]anthracene. Nearly complete sequencing of the 16S rRNA gene of strain KK22 and phylogenetic analysis revealed that this organism is a new member of the genus Sphingobium. An 8-day time course study that consisted of whole-culture extractions followed by high-performance liquid chromatography (HPLC) analyses with fluorescence detection showed that 80 to 90% biodegradation of 2.5 mg liter⁻¹ benz[a]anthracene had occurred. Biodegradation assays where benz[a]anthracene was supplied in crystalline form (100 mg liter⁻¹) confirmed biodegradation and showed that strain KK22 cells precultured on glucose were equally capable of benz[a]anthracene biotransformation when precultured on glucose plus phenanthrene. Analyses of organic extracts from benz[a]anthracene biodegradation by liquid chromatography negative electrospray ionization tandem mass spectrometry [LC/ESI(−)-MS/MS] revealed 10 products, including two o-hydroxypolyaromatic acids and two hydroxy-naphthoic acids. 1-Hydroxy-2- and 2-hydroxy-3-naphthoic acids were unambiguously identified, and this indicated that oxidation of the benz[a]anthracene molecule occurred via both the linear kata and angular kata ends of the molecule. Other two- and single-aromatic-ring metabolites were also documented, including 3-(2-carboxyvinyl)naphthalene-2-carboxylic acid and salicylic acid, and the proposed pathways for benz[a]anthracene biotransformation by a bacterium were extended.     

Beijerinckia sp strain B1: a strain by any other name . . . . .

Beijerinckia sp strain B1 grows with biphenyl as its sole source of carbon and energy. A mutant, strain B8/36, oxidized biphenyl to cis-(2S,3R)-dihydroxy-l-phenylcyclohexa-4,6-diene (cis-biphenyl dihydrodiol). Strain B8/36 oxidized anthracene, phenanthrene, benz[a]anthracene and benzo[a]pyrene to cis-dihydrodiols. Other substrates oxidized to cis-dihydrodiols were dibenzofuran, dibenzothiophene and dibenzo-p-dioxin. Biphenyl dioxygenase activity was observed in cells of Beijerinckia B1 and B8/36 after growth in the presence of biphenyl, m-, p-xylene and salicylate. Recent studies have led to the reclassification of Beijerinckia B1 as Sphingomonas yanoikuyae strain B1. Subsequent biotransformation studies showed that S. yanoikuyae B8/36 oxidized chrysene to a bis-cis-diol with hydroxyl substituents at the 3,4- and 9,10-positions. Dihydronaphthalene was oxidized to cis-1,2-dihydroxy-1,2,3,4-tetrahydronaphthalene, naphthalene, cis-1,2-dihydroxy-1,2-dihydronaphthalene and 2-hydroxy-1,2-dihydronaphthalene. Anisole and phenetole were oxidized to phenol. Thus the S. yanoikuyae biphenyl dioxygenase catalyzes cis-dihydroxylation, benzylic monohydroxylation, desaturation and dealkylation reactions. To date, the genes encoding biphenyl dioxygenase have not been cloned. However, the nucleotide sequence of a S. yanoikuyaeB1 DNA fragment contains five different α subunits as determined by conserved amino acids coordinating iron in a Rieske [2Fe-2S] center and mononuclear iron at the catalytic site. The specific role of the different putative oxygenases in biotransformation reactions catalyzed by S. yanoikuyae is not known and presents an exciting challenge for future studies. Received 29 May 1999/ Accepted in revised form 23 June 1999