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.     

A comparison of the isoelectric points of mouse liver UDP-glucuronosyltransferase enzymes conjugating the twelve benzo[a]pyrene phenols

Solubilized mouse liver microsomes were subjected to chromatofocusing using a pH 9.5 to 6.0 gradient. UDP-glucuronosyltransferase activity was assayed using 12 benzo[a]pyrene phenols as substrates. The rank of microsomal activity for the phenols was as follows: 12 > 10 > 4 > 1 > 7 > 5 > 8 > 9 > 3 > 11 > 6 > 2. Fractions separated on chromatofocusing according to isoelectric point indicated that 3-, 10-, 11-, and 12-hydroxybenzo[a]pyrene were conjugated primarily by a high pI (～8.5) activity(s), 2-, 6-, 8-, and 9-hydroxybenzo[a]pyrene were conjugated primarily by a low pI (～6.7) activity(s), and 1-, 4-, 5-, and 7-hydroxybenzo[a]pyrene were conjugated equally well by high and low pI forms.     

Metabolism of monohydroxybenzo(a)pyrenes by rat liver microsomes and mammalian cells in culture.

The 3-, 6-, and 9-monohydroxybenzo(a)pyrenes are metabolized by microsomes from rat liver in vitro. The metabolism of 3-hydroxybenzo(a)pyrene requires the presence of NADPH and is inhibited by carbon monoxide, suggesting that the reaction is mediated by a microsomal mixed-function oxygenase. The metabolic activity can be induced by in vivo treatment with 3-methylcholanthrene. 7,8-Benzoflavone strongly inhibits the induced activity but has little effect on the constitutive enzyme. The inducibility and inhibition characteristics, as well as the metabolic rate of the conversion of 3-hydroxybenzo(a)pyrene, closely resemble those of the oxidative metabolism of benzo(a)pyrene. The microsomal NADPH-dependent metabolism of [3H]3-hydroxybenzo(a)pyrene leads to the formation of a number of products of which a major fraction cochromatographs with the 3,6-quinone of benzo(a)pyrene. In mammalian cell cultures 3-hydroxybenzo(a)pyrene is converted by a mechanism different from that in hepatic microsomes. The disappearance of the phenol in cultures of hamster embryo cells is independent of the action of inducers or inhibitors of the aryl hydrocarbon hydroxylases and also occurs in the mouse L-cell line, A9, which lacks detectable aryl hydrocarbon hydroxylase activity. In A9 cells, [3H]3-hydroxybenzo(a)pyrene is largely converted to water soluble derivatives.     

Neonatal modulation of adult rat hepatic microsomal benzo[a]pyrene hydroxylase activities by Aroclor 1254 or phenobarbital

The constitutive and Aroclor 1254-induced activities of hepatic microsomal benzo[a]pyrene hydroxylases in male and female rats were determined in animals from ages 11 to 120 days. In 11-day-old noninduced male rats, benzo[a]pyrenediones and 9-hydroxybenzo[a]pyrene were the major microsomal metabolites; in 21-day-old males benzo[a]pyrene-diones and benzo[a]pyrene-9,10-dihydrodiol were predominant. In 60- and 120-day-old animals 3-hydroxybenzo[a]pyrene was the major microsomal metabolite. A similar trend was observed for the development of benzo[a]pyrene hydroxylase activities in female rats. With the exception of 4,5-dihydrodiol formation, the highest induction of individual and total benzo[a]pyrene hydroxylase activities by Aroclor 1254 was observed in the 21-day-old immature male rats, in which there was a 330- and 4.5-fold increase in the formation of 3-hydroxybenzo[a]pyrene and quinone metabolites, respectively. The induction of benzo[a]pyrene total metabolite formation by Aroclor 1254 in female rats from 11 to 120 days of age was relatively constant (i.e., 13.3- to 10.1-fold induction); however, the relative induction of the individual benzo[a]pyrene hydroxylases was highly variable. In a second set of experiments, male and female rats were neonatally exposed to phenobarbital (600 mumol/kg) or Aroclor 1254 (100 mumol/kg), and the effects of these xenobiotics on neonatal imprinting of hepatic microsomal benzo[a]pyrene hydroxylase activities were determined in the 120-day-old animals.(ABSTRACT TRUNCATED AT 250 WORDS)     

Glucuronidation of lipophilic substrates: preparation of 3-benzo[a]pyrenyl-beta-D-glucopyranosiduronic acid in multimilligram quantities by microsomal UDP-glucuronyl transferase.

A convenient method for the enzymic conversion of multimilligram quantities of 3-hydroxybenzo[a]pyrene to 3-benzo[a]pyrenyl-beta-D-glucopyranosiduronic acid in 90% yield is described. Commercially available freeze-dried rabbit liver microsomes were incubated in the presence of UDPGA, 3-hydroxybenzo[a]pyrene, and Triton X-100 detergent (Figure 1). The course of the biosynthetic reaction was followed by fluorimetry. The glucuronide product was extracted from the acidified incubation supernate with ethyl acetate and the acid function of the glucuronide was utilized in an acid-base extraction procedure to purify the glucuronide from biological and unreacted starting material. The glucuronide precipitated from ethyl acetate and was collected by centrifugation. High pressure liquid chromatography and spectroscopic techniques were used to verify the structure and purity of 3-benzo[a]pyrenyl-beta-D-glucopyranosiduronic acid.     

Purification and characterization of a benzo[a]pyrene hydroxylase from Pleurotus pulmonarius

Cytochrome P450 has been implicated in the process of biotransformation of polycyclic aromatic hydrocarbons and of other organic pollutants by white-rot fungi. We have purified and reconstituted a benzo[a]pyrene hydroxylating cytochrome P450 (P450) from microsomal fractions of the white rot fungus Pleurotus pulmonarius. The microsomal P450 was recovered using a combination of n-aminooctyl agarose and hydroxyapatite chromatography and had an apparent molecular mass of 55 kDa. The purified protein exhibited moderate affinity for benzo[a]pyrene with a K(s) of 66 microM calculated from the Type I substrate binding spectra produced. Reconstitution of activity was achieved and a turnover of 0.75 nmol 3-hydroxybenzo[a]pyrene product/min/nmol P450 was observed, comparable to levels of metabolism observed by animal cytochromes P450 involved in xenobiotic detoxification.     

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.     

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.     

Asbestos catalyzes the formation of the 6-oxobenzo[a]pyrene radical from 6-hydroxybenzo[a]pyrene

Crocidolite asbestos catalyzes the oxidation of 6-hydroxybenzo[a]pyrene, a metabolite of benzo[a]pyrene, to the 6-oxobenzo[a]pyrene radical as determined by electron spin resonance spectroscopy. This may be a mechanism whereby inhaled asbestos enhances the incidence of lung cancer induced by cigarette smoke, which contains benzo[a]pyrene.     

Glucuronidation of Lipophilic Substrates: Preparation of 3-Benzo[a]pyrenyl-β-D-glucopyranosiduronic Acid in Multimilligram Quantities by Microsomal UDP-Glucuronyl Transferase

convenient method for the enzyraic conversion of multimilli-gram quantities of 3-hydroxybenzo[a]pyrene to 3-benzo[a]pyrenyl-β-D-glucopyranosiduronic acid in 90% yield is described. Commer-cially available freeze-dried rabbit liver microsomes were incubated in the presence of UDPGA, 3-hydroxybenzo[a]pyrene, and Triton X-100 detergent (Figure 1). The course of the biosynthetic reaction was followed by fluorimetry. The glucuronide product was extracted from the acidified incubation supernate with ethyl acetate and the acid function of the glucuronide was utilized in an acid-base extraction procedure to purify the glucuronide from biological and unreacted starting material. The glucuronide pre-cipitated from ethyl acetate and was collected by centrifugation.

High pressure liquid chromatography and spectroscopic techniques were used to verify the structure and purity of 3-benzo[a]-pyrenyl-β-D-glucopyranosiduronic acid.     

Oxidation of benzo[a]pyrene by the filamentous fungus Cunninghamella elegans.

Cunninghamella elegans oxidized benzo[a]pyrene to several metabolic products. Compounds that were isolated and identified were: trans-9,10-dihydroxy-9,10-dihydrobenzo[a]pyrene, trans-7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene, benzo[a]pyrene 1,6-quinone, benzo[a]pyrene 3,6-quinone, 9-hydroxybenz[a]pyrene, and 3-hydroxybenzo[a]pyrene. In addition, an unidentified dihydroxybenzo[a]pyrene metabolite was also formed. Experiments with [14C]benzo[a]pyrene showed that over a 96-h period, 18.4% of the hydrocarbon was converted to metabolic products. Most of the metabolites were sulfate conjugates as demonstrated by the formation of benzo[a]pyrene quinones and phenols after treatment with aryl sulfatase. Glucuronide and sulfate conjugates were also detected as water-soluble metabolites. The results show that benzo[a]pyrene is metabolized by a filamentous fungus in a manner that is remarkably similar to that observed in higher organisms.     

Purification and characterization of hepatic and intestinal phenol sulfotransferase with high affinity for benzo[a]pyrene phenols from channel catfish, Ictalurus punctatus

Cytosol from channel catfish liver and intestinal mucosa has high sulfotransferase activity with low concentrations of 3-, 7-, or 9-hydroxybenzo[a]pyrene. To further investigate this conjugation pathway, sulfotransferase activity toward 9-hydroxybenzo[a]pyrene was isolated from catfish intestinal and hepatic cytosol by chromatography on anion exchange and PAP-agarose affinity columns. SDS-PAGE of the active fractions showed that one major band with molecular size of about 41,000 Da was isolated from intestine, while two bands of about 41,000 and 31,000 Da were obtained from liver. Antibodies against human phenol-sulfating sulfotransferase cross-reacted strongly with the 41,000-Da bands from liver and intestine, but weakly with the hepatic 31,000-Da protein. N-Terminal sequence information could not be obtained from the pure proteins. Following digestion, an internal sequence of 20 amino acid residues was obtained from the hepatic 41,000-Da protein, which matched a sequence found in several mammalian sulfotransferases. No fish sulfotransferase sequences were available for comparison. The identity of the hepatic 31,000-Da protein was not established. The purified 41,000-Da proteins had very high activities with 3-, 7-, or 9-hydroxybenzo[a]pyrene, with K(m) values in the 40-100 nM range and V(max) 125-300 nmol/min/mg of protein. Substrate inhibition was observed when the concentrations of hydroxylated benzo[a]pyrenes were above 0.5 microM. As well as benzo[a]pyrene phenols, the purified 41,000-Da sulfotransferases catalyzed sulfation of 2-naphthol, 4-nitrophenol, 4-methylumbelliferone, 7-(hydroxymethyl)-12-methylbenz[a]anthracene, dehydroepiandrosterone, estrone, and 17beta-estradiol. Phenolic compounds were the preferred substrates for the purified enzymes.     

Formation and removal of benzo[a]pyrene metabolites--DNA adducts in cultured normal human fibroblasts using a microsome-activating system

The rate of removal of DNA adducts of several benzo[a]pyrene metabolites from nuclear DNA was compared by introducing a microsome-activating system in human fibroblast cells. Confluent human fibroblasts were exposed to benzo[a]pyrene in the presence of a microsomal activating system and DNA adducts were formed in the nuclear DNA. The adducts present in DNA were determined after 1 h of incubation and 48 h later. There was no difference in the rate of removal between 7S- and 7R -N2-[10-(7 beta, 8 alpha-trihydroxy-7,8,9,10- tetrahydrobenzo[a]pyrene)yl]deoxyguanosine, 7R -N2-[10(7beta, 8 alpha, 9 beta-trihydroxy-7,8,9,10-tetrahydrobenzo[a]pyrene)yl]deoxyguanosine and the covalent adduct of 9-hydroxybenzo[a]pyrene-4,5-epoxide to guanosine. This finding does not agree with the idea that metabolites forming 'persistent DNA adducts' are always responsible for the carcinogenicity of their parent compound.     

A benzo[a]pyrene -7,8-dihydrodiol-9,10-epoxide is the major metabolite involved in the binding of benzo[a]pyrene to DNA in isolated viable rat hepatocytes

Benzo[a]pyrene is metabolised by isolated viable hepatocytes from both untreated and 3-methylcholanthrene pretreated rats to reactive metabolites which covalently bind to DNA. The DNA from the hepatocytes was isolated, purified and enzymically hydrolysed to deoxyribonucleosides. The hydrocarbon-deoxyribonucleoside products after initial separation, on small columns of Sephadex LH-20, from unhydrolysed DNA, oligonucleotides and free bases, were resolved by high pressure liquid chromatography (HPLC). The qualitative nature of the adducts found in both control and pretreated cells was virtually identical; however pretreatment with 3-methylcholanthrene resulted in a quantitatively higher level of binding. The major hydrocarbon-deoxyribonucleoside adduct, found in hepatocytes co-chromatographed with that obtained following reaction of the diol-epoxide, (±)7α,8β-dihydroxy-9β,10β-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene with DNA. Small amounts of other adducts were also present including a more polar product which co-chromatographed with the major hydrocarbon-deoxyribonucleoside adduct formed following microsomal activation of 9-hydroxybenzo[a]pyrene and subsequent binding to DNA. In contrast to the results with hepatocytes, when microsomes were used to metabolically activate benzo[a]pyrene, the major DNA bound-product co-chromatographed with the more polar adduct formed upon further metabolism of 9-hydroxybenzo[a]pyrene. These results illustrate that great caution must be exercised in the extrapolation of results obtained from short-term mutagenesis test systems, utilising microsomes, to in vivo carcinogenicity studies.     

Purification and immunochemical characterization of a low-pI form of UDP glucuronosyltransferase from mouse liver

A liver UDP glucuronosyltransferase (GT) enzyme from either phenobarbital- or 3-methylcholanthrene-treated C57BL/6N mice was isolated by phenyl-Sepharose, DEAE-ion exchange, and UDP hexanolamine chromatographic steps. This enzyme had a broad substrate specificity and was mainly responsible for the microsomal capacity to glucuronidate testosterone, 1-naphthol, and morphine. This UDP glucuronosyltransferase ( GTM1 ) appeared to be at least 95% homogeneous and had a subunit molecular weight of 51,000 using sodium dodecyl sulfate-polyacrylamide gel and two-dimensional gel electrophoreses. Antibodies prepared against the purified protein developed a single immunoprecipitin line by double-diffusion analysis with purified antigen and with solubilized microsomes from both control and drug-induced C57BL/6N and DBA/2N mice. A precipitin line was also observed with microsomal proteins which isoelectrofocused at approximately pH 6.7, but not with those which isoelectrofocused at approximately pH 8.5. GTM1 was, therefore, designated at low-pI form. Immunopurified antibody preferentially inhibited and immunoprecipitated GT activities toward testosterone, 1-naphthol, and morphine. To a lesser extent, activities toward phenolphthalein, 3-hydroxybenzo[a]pyrene, and estrone were inhibited while activities toward 4-nitrophenol and 4-methylumbelliferone were not affected. All activities, however, were immunoadsorbed in the presence of protein A-Sepharose. This observation can be explained by the following results. Immunoprecipitates from labeled microsomes contained primarily a 51,000-Da protein. When the immune complexes were adsorbed with protein A-Sepharose, a 54,000-Da protein as well as the expected 51,000-Da GTM1 was detected. This 54,000-Da protein was associated with the glucuronidation of 3-hydroxybenzo[a]pyrene and 4-nitrophenol, and was designated GTM2 .     

Development of a gas chromatography/mass spectrometry method to quantify several urinary monohydroxy metabolites of polycyclic aromatic hydrocarbons in occupationally exposed subjects

The aim of this study was the development of a method for the determination of 12 urinary monohydroxy metabolites of PAHs, namely 1-hydroxynaphthalene, 2-hydroxynaphthalene, 2-hydroxyfluorene, 9-hydroxyfluorene, 1-hydroxyphenanthrene, 2-hydroxyphenanthrene, 3-hydroxyphenanthrene, 4-hydroxyphenanthrene, 9-hydroxyphenanthrene, 1-hydroxypyrene, 6-hydroxychrysene, and 3-hydroxybenzo[a]pyrene. Analytes were determined in the presence of deuterated analogues as internal standards, by GC/MS operating in the electron impact mode. Sample preparation was performed by enzymatic hydrolysis of glucoronate and sulphate conjugates of hydroxy metabolites of PAHs, liquid-liquid extraction with n-hexane, and derivatization with a silylating reagent. The method is very specific, limits of quantification are in the range 0.1-1.4 microg/l, and range of linearity is from limit of detection to 208 microg/l. Within- and between-run precision, expressed as coefficient of variation, are <20%; accuracy for most analytes is within 20% of the theoretical value. An application of the proposed method to the analysis of 10 urine samples from coke-oven workers shows that 1-hydroxynaphthalene and 2-hydroxyfluorene were the most abundant compounds (median 61.4 and 69.7 microg/l, respectively), while 6-hydroxychrysene, and 3-hydroxybenzo[a]pyrene were always below the quantification limit.     

Protein engineering of cytochrome p450(cam) (CYP101) for the oxidation of polycyclic aromatic hydrocarbons

Mutations of the active site residues F87 and Y96 greatly enhanced the activity of cytochrome P450(cam) (CYP101) from Pseudomonas putida for the oxidation of the polycyclic aromatic hydrocarbons phenanthrene, fluoranthene, pyrene and benzo[a]pyrene. Wild-type P450(cam) had low (<0.01 min(-1)) activity with these substrates. Phenanthrene was oxidized to 1-, 2-, 3- and 4-phenanthrol, while fluoranthene gave mainly 3-fluoranthol. Pyrene was oxidized to 1-pyrenol and then to 1,6- and 1,8-pyrenequinone, with small amounts of 2-pyrenol also formed with the Y96A mutant. Benzo[a]pyrene gave 3-hydroxybenzo[a]pyrene as the major product. The NADH oxidation rate of the mutants with phenanthrene was as high as 374 min(-1), which was 31% of the camphor oxidation rate by wild-type P450(cam), and with fluoranthene the fastest rate was 144 min(-1). The oxidation of phenanthrene and fluoranthene were highly uncoupled, with highest couplings of 1.3 and 3.1%, respectively. The highest coupling efficiency for pyrene oxidation was a reasonable 23%, but the NADH turnover rate was slow. The product distributions varied significantly between mutants, suggesting that substrate binding orientations can be manipulated by protein engineering, and that genetic variants of P450(cam) may be useful for studying the oxidation of polycyclic aromatic hydrocarbons by P450 enzymes.     

The conversion of benzo(alpha)pyrene 4,5-oxide into 4-hydroxybenzo(alpha)pyrene in the presence of polyriboguanylic acid.

Incubation of benzo[alpha] pyrene 4,5-oxide with poly(G) in neutral aqueous ethanol resulted in the formation of covalent adducts and in the production of free 4-hydroxybenzo[alpha]pyrene. This phenol, which was identified by its UV spectral properties and by its chromatographic characteristics, was also formed but at a much slower rate when the epoxide was incubated with DNA or with GMP. Phenol formation was not detected when benzo[alpha]-pyrene 4,5-oxide was incubated for prolonged periods in the presence of poly(A), poly(C) or poly(U) or in the absence of nucleic acid. Formation of 4-hydroxybenzo[alpha] pyrene from the epoxide in the presence of poly(G) was not accompanied by detectable base modifications or by breakage of phosphodiester linkages.     

Metabolism of xenobiotic compounds by enzymes in cell extracts of the fungus Cunninghamella elegans.

Cell extracts of the filamentous fungus Cunninghamella elegans contain epoxide hydrolase (EC 3.3.2.3), glutathione S-transferase (EC 2.5.1.18) and UDP-glucuronosyltransferase (EC 2.4.1.17) activities. Epoxide hydrolase activity was determined with p-nitrostyrene oxide as substrate and was shown to be associated with the 100 000 g pellet obtained from disrupted mycelia. Glutathione S-transferase activity was demonstrated with 1-chloro-2,4-dinitrobenzene and p-nitrobenzyl chloride as substrates. The presence of two or more glutathione S-transferase activities was indicated by different activity ratios for the two substrates in different extracts, and by distinct thermal denaturation curves. UDP-glucuronosyltransferase activity with 3-hydroxybenzo[a]pyrene as substrate was found only with the non-sedimentable fraction prepared from ruptured mycelia.     

Phenols as toxic metabolites of benz(a)pyrene

The effect of benzo(a)pyrene and two its phenolic metabolites 3-hydroxybenzo(a)-pyrene and 6-hydroxybenzo(a)pyrene--on the cultures of normal and transformed fibroblasts has been studied. In was shown that unlike the parent carcinogen its phenolic metabolites exerted only toxic (but not transforming) effect on cultured cells, and this effect has been developed at a faster rate than that produced by benzo(a)pyrene. 6-hydroxybenzo(a)pyrene was more toxic than 3-hydroxybenzo(a) pyrene. It was concluded that both metabolites produced their effects without preliminary activation by microsomal enzymes.