Covalent binding of benzo[a]pyrene to dna in fish liver

Benzo[a]pyrene became bound to the hepatic DNA in juvenile English sole ($\text{Parophrys vetulus}$) force fed tritiated benzo[a]pyrene. No statistically signïficant change was observed in the level of the binding from 16 h to 2 wk after the single exposure. Specific activities of binding were similar for both DNA and protein. Moreover, a binding index was calculated to represent the number of benzo[a]pyrene molecules bound per 10⁶ nucleotides after administration of a theoretical dose of 1 mmole of hydrocarbon per kg body weight. The value for English sole liver DNA was of the same order of magnitude as the values reported for mouse skin and mammary gland in which benzo[a]pyrene is carcinogenic.     

Non-enzymatic ATP-mediated binding of hydroxymethyl derivatives of aromatic hydrocarbons to DNA

ATP mediates covalent binding of hydroxymethyl derivatives of aromatic hydrocarbons to DNA. This non-enzymatic reaction has been studied with 6-[14C]hydroxymethylbenzo[alpha]pyrene (]14C]BP-6-CH2OH) and 7-[14C]-hydroxymethylbenz[alpha]anthracene ([14C]BA-7-CH2OH) at 37 degrees C in Tris buffer (pH 7.0). While ADP mediates the reaction 25-50% as well as ATP, six other possible phosphate donors including AMP were inactive as cofactors. A complex response to ATP occurred in which low binding of BP-6-CH2OH or BA-7-CH2OH was observed at concentrations of ATP below 2.5 mM, but a greater than linear response to higher concentrations of ATP was observed until ATP was saturating. Binding of the substrates to RNA was much lower than to DNA. Fluorescence spectra of BP-6-CH2OH bound to DNA were almost identical to the spectra of 6-bromomethylbenzo[alpha]pyrene bound to DNA and free 6-methylbenzo]alpha]pyrene, indicating that ATP-mediated binding of BP-6-CH2OH to DNA occurs at the 6-methyl group. The fate of ATP and ADP in the binding reaction of BP-6-CH2OH was examined by thin layer chromatography. Loss of one phosphate group occurs during the reaction. With ATP the rate of loss is about 100-fold greater than the rate of binding of BP-6-CH2OH to DNA. This implies that the binding reaction proceeds through formation of a presumed reactive and unstable phosphate ester intermediate which then inefficiently binds to DNA.     

Purification of a benzo[a]pyrene binding protein by affinity chromatography and photoaffinity labeling

Binding proteins for the polycyclic aromatic hydrocarbon carcinogen benzo[a]pyrene (B[a]P) have been purified from C57B1/6J mouse liver. Following affinity chromatography on aminopyrene-Sepharose, a single polypeptide of 29,000 daltons was isolated. The photolabile compound 1-azidopyrene was developed as a photoaffinity labeling agent to identify the protein during its purification. 1-Azidopyrene was found to be a competitive inhibitor of [3H]B[a]P binding. Affinity labeling studies with [3H]-1-azidopyrene in unfractionated cytosol, and in purified preparations, yielded a single covalently labeled protein of 29,000 daltons. The formation of this labeled species was blocked by preincubation with excess unlabeled B[a]P. A native molecular weight of 30,000 was estimated by gel filtration chromatography of [3H]B[a]P- and [3H]-1-azidopyrene-labeled cytosol proteins. An equilibrium dissociation constant of 2.69 +/- 0.66 nM and a maximum number of binding sites of 2.07 +/- 0.10 nmol of [3H]B[a]P bound/mg of protein were estimated for the pure protein. Two-dimensional gel electrophoresis further resolved the purified 29,000-dalton protein into three major isoelectric variants, each of which was specifically labeled by [3H]-1-azidopyrene.     

Carcinogenicity and metabolic profiles of 6-substituted benzo[a]pyrene derivatives on mouse skin

The ability was tested of appropriate substituents of benzo[a]pyrene (BP) at C-6 to decrease or suppress the carcinogenic activity for these BP derivatives relative to the parent compound. 8-week-old female Swiss mice in 9 groups of 30 were treated on the back with 0.2 mumol of compound in acetone 4 times weekly for 20 weeks. The following compounds were administered: BP, 6-methylbenzo[a]pyrene (BP-6-CH3), 6-hydroxymethylbenzo[a]pyrene (BP-6-CH2OH), benzo[a]pyrene-6-carboxaldehyde (BP-6-CHO), benzo[a]pyrene-6-carboxylic acid, 6-methoxybenzo[a]pyrene, 6-acetoxybenzo[a]pyrene, 6-bromobenzo[a]pyrene, and 6-iodobenzo[a]pyrene. Two additional groups received BP or BP-6-CH3 twice weekly for 20 weeks at a total dose 25% of that above. In addition, the metabolism of selected 6-substituted BP derivatives was studied, using mouse skin homogenates in vitro and mouse skin in vivo. Only four compounds were carcinogenic; the order of potency was BP greater than BP-6-CH3 greater than BP-6-CH2OH and BP-6-CHO. The difference in carcinogenicity between BP-6-CH2OH and BP-6-CHO could not be assessed by this experiment. In a further tumorigenesis experiment the carcinogenicity of BP-6-CH2OH was compared to that of BP-6 CHO, BP-6-CH3 and 6-hydroxymethylbenzo[a]pyrere sulfate ester (BP-6-CH2OSO3Na) on mouse skin. 9-week-old female Swiss mice in groups of 28 were treated at three dose levels with 0.8, 0.2 and 0.05 mumol of compounds in dioxane--dimethyl sulfoxide (75 : 25) twice weekly for 40 weeks. After 40 experimental weeks BP-6-CH2OSO3Na proved to be a more potent carcinogen than BP-6-CH2OH, which, in turn was more active than BP-6-CHO. The greater carcinogenicity of BP-6-CH3 relative to BP-6-CH2OH and BP-6-CHO is confirmed, suggesting that BP-6-CH2OH is not a proximate carcinogenic metabolite for BP-6-CH3. Since BP-6-CHO is a weaker carcinogen than BP-6-CH2OH and is efficiently reduced metabolically to BP-6-CH2OH, the latter compound may be a common proximal carcinogenic metabolite. The stronger potency of BP-6-CH2OSO3Na, compared to its alcohol, suggests that an ester of BP-6-CH2OH might be the ultimate alkylating compound reacting with cellular nucleophiles.     

Decay-associated emission spectra and other spectral evidence for the physical intercalation of 7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene into DNA

A benzo[a]pyrene derivative, 7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene, forms physical complexes with DNA. The measured absorption spectrum of the hydrocarbon in the complex is shifted approximately 10 nm to the red and the fluorescence emission spectrum is red-shifted approximately 6 nm, characteristic of a physical intercalation complex. The decay-associated emission spectra of the hydrocarbon in the presence of DNA have been measured, thus providing a new technique to obtain information about the DNA binding sites. The decay-associated emission spectra of the free and bound hydrocarbons were obtained by deconvoluting the time-dependent emission at several wavelengths. Stern-Volmer plots with iodide and silver ions as quenchers suggest that at least one set of binding sites for the formation of a physical intercalation complex between the benzo[a]pyrene derivative and DNA is at guanine sites in the biopolymer.     

Mutagenic activity of biliary metabolites of 6-hydroxymethylbenzo[a]pyrene

The biliary excretion of the carcinogen 6-hydroxy-methylbenzo[a]pyrene was investigated in rats after i.p. administration. Mutagenicity of the parent compound and its biliary metabolites was tested in Ames Salmonella/microsome mutagenicity assay. Approximately 40% of the dose administered (0.25-0.5 mg/kg) to the rats was excreted in the bile within 6 h. 6-Hydroxymethylbenzo[a]pyrene was excreted primarily as water-soluble metabolites, including glucuronide and sulfate conjugates. Negligible quantities of unchanged 6-hydroxymethylbenzo[a]pyrene were excreted in the bile. In the presence of Aroclor-induced S9, 6-hydroxymethylbenzo[a]pyrene was a potent mutagen. The mutagenicity of bile from rats treated with 6-hydroxymethylbenzo[a]pyrene was variable in the absence of an activation system. However, the same bile samples were mutagenic in the presence of beta-glucuronidase and/or S9. These results indicate that biliary metabolites of 6-hydroxymethylbenzo[a]pyrene can be metabolically activated to mutagenic species.     

DNA--benzo[a]pyrene adducts formed in a Salmonella typhimurium mutagenesis assay system.

The DNA adducts formed in Salmonella typhimurium when bacteria are incubated with radioactive benzo[a]pyrene and liver microsomal enzymes from several sources has been investigated. When enzyme preparations from Aroclor I254 or 3-methylcholanthrene induced C57BL/6N (B6) mice were used to mediate activation, the predominant product was an adduct between the 10 position of 7 beta, 8 alpha-dihydroxy-9 alpha, 10 alpha epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene and the N-2 position of deoxyguanosine. Similar results were obtained with human liver and with Aroclor-induced rat-liver enzyme preparations. This adduct is also the major DNA product previously found when human tissues or certain rodent cells were incubated with benzo[a]pyrene. On the other hand, when activation of benzo[a]pyrene was mediated by a phenobarbital-induced B6 mouse-liver enzyme preparation, the extent of binding was quite low and the profile of DNA adducts in S. typhimurium DNA was quite different. Thus, under appropriate conditions, the activation and DNA binding of benzo[a]pyrene inthe microsome mediated S. typhimurium mutagenesis assay generally resembles that seen in intact mammalian cells. Caution must be exercised, however, in the choice of microsome-activation systems.     

Sequence-specific modification of DNA by 6-hydroxybenzo[a]pyrene

6-Hydroxybenzo[a]pyrene cleaved phi X174 supercoiled DNA to open circular DNA in the presence of heavy metal ions. It induced an alkali-labile modification in DNA via an oxygen-radical-mediated reaction; the most frequent alkali-labile sites were on the 3' side of the pyrimidine residues of the pyrimidine cluster.     

Equilibrium binding of benzo[a]pyrene tetrol to synthetic polynucleotides: sequence selectivity, thermodynamic properties, and ionic strength dependence

We have investigated the equilibrium binding of racemic 7r,8t,9t,10c-tetrahydroxy-7,8,9,10-tetrahydrobenzo[a]pyrene to the double-stranded, synthetic polynucleotides poly[d(A-T)], poly[d(G-C)], and poly[d(G-m5C)] at low binding ratios. Difference absorption spectroscopy shows a 10-nm red shift for binding to poly[d(A-T)] and an 11-nm red shift for binding to either poly[d(G-C)] or poly[d(G-m5C)]. The value of delta epsilon for binding is approximately the same for all three hydrocarbon-polynucleotide complexes. Binding of this neutral polycyclic aromatic hydrocarbon derivative to these polynucleotides is dependent upon ionic strength and temperature. Analysis of complex formation employing polyelectrolyte theory shows a greater release of counterions associated with binding to poly[d(A-T)] than with the other two polynucleotides (0.5 and ca. 0.36, respectively). Thus, sequence-selective binding of this hydrocarbon in DNA would be expected to change depending on salt concentration. The temperature dependence of binding was studied at 100 mM Na+ where the equilibrium binding constants for poly[d(A-T)] and poly[d(G-m5C)] are roughly equivalent and 6-fold greater than the binding affinity for poly[d(G-C)]. The binding to poly[d(A-T)] and poly[d(G-C)] is characterized by a delta H omicron = -7.0 kcal/mol, and the large difference in affinity constants arises from differences in negative entropic contributions. Formation of hydrocarbon-poly[d(G-m5C)] complexes is accompanied by a delta H = -9.1 kcal/mol. However, the affinity for poly[d-(G-m5C)] is the same as that for poly[d(A-T)] due to the much more negative entropy associated with binding to poly[d(G-m5C)].     

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.     

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.     

The strong hepatocarcinogenicity of the electrophilic and mutagenic metabolite 6-sulfooxymethylbenzo[a]pyrene and its formation of benzylic DNA adducts in the livers of infant male B6C3F1 mice

6-Hydroxymethylbenzo[a]pyrene was activated to an electrophilic and mutagenic sulfuric acid ester metabolite by rat and mouse liver sulfotransferase activity. The intrinsic mutagenicity of this reactive ester, 6-sulfooxymethylbenzo[a]pyrene, was inhibited by glutathione and glutathione S-transferase. A single i.p. dose of 2.5 nmol/g body wt of 6-sulfooxymethylbenzo[a]pyrene in infant male B6C3F1 mice induced liver tumors in 35 of 36 mice at 10 months with an average multiplicity of 4.4. A comparable dose of the parent hydrocarbon, 6-hydroxymethylbenzo[a]pyrene, was only a tenth as active. The electrophilic sulfuric acid ester produced high levels of benzylic DNA adducts in the livers of these mice that accounted for about 80% of the total DNA adducts. These results strongly suggest that this sulfuric acid ester is an important ultimate electrophilic and carcinogenic metabolite in carcinogenesis by 6-hydroxymethylbenzo[a]pyrene and possibly even by 6-methylbenzo[a]pyrene and benzo[a]pyrene in mouse liver.     

Dnmt3a-CD is less susceptible to bulky benzo[a]pyrene diol epoxide-derived DNA lesions than prokaryotic DNA methyltransferases

Benzo[a]pyrene (B[a]P) is a well-characterized environmental polycyclic aromatic hydrocarbon pollutant. In living organisms, B[a]P is metabolized to the genotoxic anti-benzo[a]pyrene diol epoxide that reacts with cellular DNA to form stereoisomeric anti-B[a]PDE-N(2)-dG adducts. In this study, we explored the effects of adduct stereochemistry and position in double-stranded DNA substrates on the functional characteristics of the catalytic domain of murine de novo DNA methyltransferase Dnmt3a (Dnmt3a-CD). A number of 18-mer duplexes containing site-specifically incorporated (+)- and (-)-trans-anti-B[a]PDE-N(2)-dG lesions located 3'- and 5'-adjacent to and opposite the target cytosine residue were prepared. Dnmt3a-CD binds cooperatively to the DNA duplexes with an up to 5-fold greater affinity compared to that for the undamaged DNA duplexes. Methylation assays showed a 1.7-6.3-fold decrease in the methylation reaction rates for the damaged duplexes. B[a]PDE modifications stimulated a nonproductive binding and markedly favored substrate inhibition of Dnmt3a-CD in a manner independent of DNA methylation status. The latter effect was sensitive to the position and stereochemistry of the B[a]PDE-N(2)-dG adducts. The overall effect of trans-anti-B[a]PDE-N(2)-dG adducts on Dnmt3a-CD was less detrimental than in the case of the prokaryotic methyltransferases we previously investigated.     

Metabolism of benzo[a]pyrene VI. Stereoselective metabolism of benzo[a]pyrene and benzo[a]pyrene 7,8-dihydrodiol to diol epoxides

(±)-7β,8α-Dihydroxy-9β,10β-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene (diol epoxide-1) and (±)-7β,8α-dihydroxy-9α,10α-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene (diol epoxide-2) are highly mutagenic diol epoxide diastereomers that are formed during metabolism of the carcinogen (±)-trans-7,8-dihydroxy-7,8-dihydrobenzo[a]pyrene. Remarkable stereoselectivity has been observed on metabolism of the optically pure (+)- and (?)-enantiomers of the dihydrodiol which are obtained by separation of the diastereomeric diesters with (?)-α-methoxy-α-trifluoromethylphenylacetic acid. The high stereoselectivity in the formation of diol epoxide-1 relative to diol epoxide-2 was observed with liver microsomes from 3-methylcholanthrene-treated rats and with a purified cytochrome P-448-containing monoxygenase system where the (?)-enantiomer produced a diol epoxide-2 to diol epoxide-1 ratio of 6 : 1 and the (+)-enantiomer produced a ratio of 1 : 22. Microsomes from control and phenobarbital-treated rats were less stereospecific in the metabolism of enantiomers of BP 7,8-dihydrodiol. The ratio of diol epoxide-2 to diol epoxide-1 formed from the (?)- and (+)-enantiomers with microsomes from control rats was 2 : 1 and 1 : 6, respectively. Both enantiomers of BP 7,8-dihydrodiol were also metabolized to a phenolic derivative, tentatively identified as 6,7,8-trihydroxy-7,8-dihydrobenzo[a]pyrene, which accounted for ～30% of the total metabolites formed by microsomes from control and phenobarbital-pretreated rats whereas this metabolite represents ～5% of the total metabolites with microsomes from 3-methylcholanthrene-treated rats. With benzo[a]pyrene as substrate, liver microsomes produced the 4,5-, 7,8- and 9,10-dihydrodiol with high optical purity (>85%), and diol epoxides were also formed. Most of the optical activity in the BP 7,8-dihydrodiol was due to metabolism by the monoxygenase system rather than by epoxide hydrase, since hydration of (±)-benzo[a]pyrene 7,8-oxide by liver microsomes produced dihydrodiol which was only 8% optically pure. Thus, the stereospecificity of both the monoxygenase system and, to a lesser extent, epoxide hydrase plays important roles in the metabolic activation of benzo[a]pyrene to carcinogens and mutagens.     

Inhibition of epidermal metabolism and DNA-binding of benzo[a]pyrene by ellagic acid

Ellagic acid, a common plant phenol, was shown to be a potent inhibitor of epidermal microsomal aryl hydrocarbon hydroxylase (AHH) activity in vitro, and of benzo[a]pyrene (BP)-binding to both calf thymus DNA in vitro and to epidermal DNA in vivo. The in vitro addition of ellagic acid (0.25-2.0 microM) resulted in a dose-dependent inhibition of AHH activity in epidermal microsomes prepared from control or carcinogen-treated animals. The I50 of ellagic acid for epidermal AHH was 1.0 microM making it the most potent inhibitor of epidermal AHH yet identified. In vitro addition of ellagic acid to microsomal suspensions prepared from control or coal tar-treated animals resulted in 90% inhibition of BP-binding to calf thymus DNA. Application of ellagic acid to the skin (0.5-10.0 mumol/10 gm body wt) caused a dose-dependent inhibition of BP-binding to epidermal DNA. Our results suggest that phenolic compounds such as ellagic acid may prove useful in modulating the risk of cutaneous cancer from environmental chemicals.     

Investigation of absorption, metabolism kinetics and DNA-binding of intratracheally administered benzo[a]pyrene in the isolated, perfused rat lung: a comparative study between microcrystalline and particulate adsorbed benzo[a]pyrene

Benzo[a]pyrene (B[a]P) adsorbed onto urban air particles (UAP) or in microcrystalline form (MCr) was administered intratracheally to the isolated perfused lung in doses of 100 and 1.5 micrograms. The appearance rate constant calculated for B[a]P release to the perfusate buffer was significantly lower for B[a]P administered adsorbed onto UAP (0.007 +/- 0.002 min-1) compared to the microcrystalline preparation (0.051 +/- 0.030 min-1). A classical two-compartmental model fitted well to the elimination of B[a]P from the perfusate buffer, after administration in solution to the buffer reservoir; C = 24 e-0.05t + 14 e-0.01t (pmol/ml). The concentration of polar metabolites in the perfusion buffer, at the end of experiments was approx. 9-fold higher for lungs administered the microcrystalline preparation compared to UAP at 1.5 microgram doses. At the 100 microgram dose level, the difference between preparations was only 2-fold, the data indicating that enzyme saturation might be important at the high dose level. With regard to the metabolite pattern, adsorption of B[a]P onto urban air particles caused a relative increase in the formation of B[a]P-9,10-dihydrodiol, whereas the relative formation rate for phenols was decreased. The absolute levels of B[a]P metabolites covalently bound to DNA was significantly higher in lungs given the MCr preparation compared to the UAP. When calculated as the amount metabolites bound, in relation to the total amount polar metabolites at the end of perfusion, however, the UAP preparation was significantly more efficient to enhance the production of DNA binding metabolites; 2.62 +/- 0.59 X 10(-5) vs. 1.33 +/- 0.21 X 10(-5) (pmol covalently DNA-bound metabolites/mg DNA/pmol metabolites formed). The results indicate that urban air particles may exert a cocarcinogenic effect with polynuclear aromatic hydrocarbons by increasing the pulmonary residence time for the carcinogenic hydrocarbon and/or alter the metabolite pattern in a way that enhances the covalent binding of metabolites to DNA.     

Effects of harman and norharman on the mutagenicity and binding to DNA of benzo[a]pyrene metabolites in vitro and on aryl hydrocarbon hydroxylase induction in cell culture

Harman and norharman, two β-carboline derivatives known to exist in certain foods and to be formed during pyrolysis of tobacco and meat, were tested for mutagenic activity in the presence of benzo[a]pyrene, mouse liver enzymes, and Salmonella typhimurium TA98 in vitro. Both harman and norharman inhibit benzo[a]pyrene mutagenicity, benzo[a]pyrene metabolism (as measured by aryl hydrocarbon hydroxylase activity), and the binding of all benzo[a]pyrene metabolites to DNA in vitro. Moreover, harman and norharman are quite toxic to cultures of hepatoma-derived H-4-II-E and Hepa-1 established cell lines and therefore were found to be very weak inducers of aryl hydrocarbon hydroxylase activity.     

Factors Influencing the Photodynamic Action of Benzo[a]pyrene on Escherichia coli

Death of Escherichia coli resulted when a buffer suspension was exposed simultaneously to colloidal benzo[a]pyrene (BP) and 355-mmu illumination. Neither hydrocarbon nor illumination alone caused death; oxygen had to be present. The survival curve had a shoulder, and then death proceeded exponentially with time. Death rate was independent of temperature between 6 and 32 C. The duration of the shoulder, however, decreased slightly with increase in temperature. The shoulder was not due to delay in BP entering the cell. Death was influenced by the composition of the medium in which the cells were grown prior to illumination. The amount of BP bound to the cells was determined after three ethyl alcoholether extractions. Appreciable binding occurred in the presence of 355-mmu illumination with air, and relatively little binding occurred under nitrogen; very little binding occurred in the dark with nitrogen or air. At the outset, rate of binding under illumination with air was not temperature-dependent, but with time it became strongly temperature-dependent. Binding under illumination with nitrogen was temperature-independent. Bound BP was associated primarily with cell protein. Cells in growth medium resisted death and BP binding. At 21 and 32 C, deoxyribonucleic acid damage occurred during exponential death. No damage was detected at 21 and 32 C in the dark with BP, under illumination in absence of BP, or under illumination with BP in a nitrogen atmosphere.     

Nitroreduction of 6-nitrobenzo[a]pyrene: a potential activation pathway in humans

6-Nitrobenzo[a]pyrene, an environmental pollutant, was metabolized by human intestinal microflora to 6-nitrosobenzo[a]pyrene and 6-aminobenzo[a]pyrene. The two-electron reduction product 6-nitrosobenzo[a]pyrene exhibited strong direct-acting mutagenicity in the Salmonella typhimurium assay. These results imply that 6-nitrobenzo[a]pyrene can be hazardous to human health via a nitroreduction activation pathway and opens the possibility that other nitro-polycyclic aromatic hydrocarbons that are not direct-acting mutagens may be activated in vivo by a similar mechanism.     

Rat liver homogenate (S9)-mediated binding of benzo[a]pyren to DNA in V79 cells,V79 cell nuclei and aqueous solution

The role of the target cell in determining the structures and the amounts of hydrocarbon-DNA adducts formed after hydrocarbon activation by an exogenous metabolic ativation system was investigated by exposing intact cells of the Chinese hamster lung cell line V79, V79 cell nuclei and calf thymus DNA to benzo[a]pyrene (B[a]P) in the presenceof a rat liver homogenate activation system (S9). The DNA was isolated, enzymatically degraded to deoxyribonucleosides and the B[a]P-deoxyribonucleoside adducts analyzed by high-performance liquid chromatography. Two major adducts were present in all samples; one formed by reaction of r-7, t-8-dihydroxy-t-9, 10-epoxy-7, 8, 9, 10-tetrahydro-B[a]P (anti-B[a]PDE) with the 2-amino group of deoxyguanosine, the other formed by reaction of a metabolite of 9-hydroxybenzo[a]pyrene (9-OH-B[a]P) with an unidentified deoxyribonucleoside. The ratios of the anti-B[a]PDE-DNA adduct to the 9-OH-B[a]P-DNA adduct were: calf thymus DNA, 3 to 1: DNA from V79 nuclei, 8 to 1; DNA from intact V79 cells, 11 to 1. Similar several-fold increases in the proportion of anti-B[a]PDE-DNA adducts in V79 cells over those in calf thymus DNA were observed for a dose range of 1–10 μg B[a]P per ml. The relative extent of binding of the activated metabolite of 9-OH-B[a]P to DNA was also much lower in intact V79 cells than in calf thymus DNA after exposure to 9-OH-B[a]P in the presence of the S9 activation system.These results demonstrate that the relative abilities of various reactive bbenzo[a]pyrene metabolites formed by an exogenous activation system to reach DNA differ substantially. Therefore, assessment of the biological activity of hydrocarbons in mutation assays using exogenous activation systems must take into account not only the amounts of different reactive hydrocarbon metabolites formed but also the relative abilities of these metabolites to reach the DNA of the target cell.