Tumor-initiating activity and carcinogenicity of dibenzo[a,l]pyrene versus 7,12-dimethylbenz[a]anthracene and benzo[a]pyrene at low doses in mouse skin

Dibenzo[a,l]pyrene (DB[a,l]P) is an extremely potent carcinogen that may be present in environmental samples. Dose-response studies were conducted at low doses in mouse skin by initiation-promotion and repeated application to compare its activity to that of 7,12-dimethylbenz[a]anthracene (DMBA), benzo[a]pyrene (B[a]P), DB[a,l]P-8,9-dihydrodiol and DB[a,l]P-11,12-dihydrodiol. Female SENCAR mice were initiated with 1 or 0.25 nmol of DB[a,l]P, DMBA, B[a]P or DB[a,l]P-11,12-dihydrodiol and promoted with phorbol ester acetate. At 1 nmol, DB[a,l]P induced 2.6 tumors/mouse, whereas DB[a,l]P-11,12-dihydrodiol and DMBA induced 0.17 and 0.29 tumors/mouse respectively. At the low dose, DB[a,l]P induced 0.79 tumors/mouse, but the other two compounds were virtually inactive. B[a]P, tested only at 1 nmol, was inactive. These three compounds, as well as DB[a,l]P-8,9-dihydrodiol, were tested by repeated application twice weekly for 40 weeks at 1 and 4 nmol per dose. In addition, DB[a,l]P, DMBA and B[a]P were also tested at 8 nmol. At 8 and 4 nmol, DB[a,l]P induced malignant tumors in 91 and 70% of mice respectively. At 4 nmol DB[a,l]P-11,12-dihydrodiol elicited only benign tumors in 36% of mice. At 4 nmol DMBA induced two carcinomas in one mouse and at 8 nmol it induced one papilloma and one sebaceous gland adenoma. B[a]P and DB[a,l]P-8,9-dihydrodiol were inactive at all doses tested. These results demonstrate that DB[a,l]P is a much more potent carcinogen than DMBA, the aromatic hydrocarbon previously considered to be the most potent. Combination of these results with previous comparisons of DB[a,l]P, DB[a,l]P-11,12-dihydrodiol, DMBA and B[a]P at higher doses (E.L. Cavalieri et al. (1991) Carcinogenesis, 12, 1939-1944) shows clearly the interference of toxicity with the tumorigenicity of DB[a,l]P and its 11,12-dihydrodiol.

Identification and quantitation of 7,12-dimethylbenz[a]anthracene-DNA adducts formed in mouse skin

Identification and quantitation of the depurination and stable DNA adducts of 7,12-dimethylbenz[a]anthracene (DMBA) formed by cytochrome P450 in rat liver microsomes previously established one-electron oxidation as the predominant mechanism of activation of DMBA to bind to DNA. In this paper we report the identification and quantitation of the depurination and stable DMBA-DNA adducts formed in mouse skin. The depurination adducts, which constitute 99% of all the adducts detected, are DMBA bound at the 12-methyl group to the N-7 of adenine or guanine, namely, 7-methylbenz[a]anthracene (MBA)-12-CH2-N7Ade and 7-MBA-12-CH2-N7Gua. The depurination adducts were identified by HPLC and fluorescence line narrowing spectroscopy. The stable DNA adducts were analyzed by the 32P-postlabeling method. Almost 4 times as much of the depurination adduct 7-MBA-12-CH2-N7Ade (79%) was formed compared to 7-MBA-12-CH2-N7Gua (20%). The stable adducts accounted for only 1% of all the adducts detected and 80% of these were formed from DMBA diolepoxide. The binding of DMBA to DNA specifically at the 12-CH3 group is consistent with the results of carcinogenicity experiments in which this group plays a key role. When DMBA was bound to RNA or denatured DNA in reactions catalyzed by microsomes or by horseradish peroxidase (HRP), no depurination DNA adducts of DMBA were detected. The amount of stable DNA adducts observed with denatured DNA was 70% lower in the HRP system and 30% lower in the microsomal system compared to native DNA.(ABSTRACT TRUNCATED AT 250 WORDS)

Identification of C8-methylguanine in the hydrolysates of DNA from rats administered 1,2-dimethylhydrazine. Evidence for in vivo DNA alkylation by methyl radicals

C8-Methylguanine was identified in the neutral hydrolysates of DNA isolated from the liver or colon tissue of rats administered 1,2-dimethylhydrazine. In all the samples examined, the biologically isolated adducts were characterized by co-elution with synthetic C8-methylguanine under different high pressure liquid chromatography conditions. The sample isolated from liver DNA was also identified by UV spectroscopy at different pH values and by mass spectrometry. The estimated yields of C8-methylguanine obtained in hydrolysates of DNA from the liver or colon tissue were comparable to those of O6-methylguanine. C8-Methylguanine was not detected when the spin trap alpha-(4-pyridyl-1-oxide)-N-tert- butylnitrone was administered together with 1,2-dimethylhydrazine. The spin trap also inhibited N7-methylguanine and O6-methylguanine yields, although to a lesser extent. These results constitute the first evidence that DNA alkylation by carbon-centered radicals can occur in vivo.

Identification and quantitation of benzo[a]pyrene-DNA adducts formed by rat liver microsomes in vitro

The two DNA adducts of benzo[a]pyrene (BP) previously identified in vitro and in vivo are the stable adduct formed by reaction of the bay-region diol epoxide of BP (BPDE) at C-10 with the 2-amino group of dG (BPDE-10-N2dG) and the adduct formed by reaction of BP radical cation at C-6 with the N-7 of Gua (BP-6-N7Gua), which is lost from DNA by depurination. In this paper we report identification of several new BP-DNA adducts formed by one-electron oxidation and the diol epoxide pathway, namely, BP bound at C-6 to the C-8 of Gua (BP-6-C8Gua) and the N-7 of Ade (BP-6-N7Ade) and BPDE bound at C-10 to the N-7 of Ade (BPDE-10-N7Ade). The in vitro systems used to study DNA adduct formation were BP activated by horseradish peroxidase or 3-methylcholanthrene-induced rat liver microsomes, BP 7,8-dihydrodiol activated by microsomes, and BPDE reacted with DNA. Identification of the biologically-formed depurination adducts was achieved by comparison of their retention times on high-pressure liquid chromatography in two different solvent systems and by comparison of their fluorescence line narrowing spectra with those of authentic adducts. The quantitation of BP-DNA adducts formed by rat liver microsomes showed 81% as depurination adducts: BP-6-N7Ade (58%), BP-6-N7Gua (10%), BP-6-C8Gua (12%), and BPDE-10-N7Ade (0.5%). Stable adducts (19% of total) included BPDE-10-N2dG (15%) and unidentified adducts (4%). Microsomal activation of BP 7,8-dihydrodiol yielded 80% stable adducts, with 77% as BPDE-10-N2dG and 20% of the depurination adduct BPDE-10-N7Ade. The percentage of BPDE-10-N2dG (94%) was higher when BPDE was reacted with DNA, and only 1.8% of BPDE-10-N7Ade was obtained.(ABSTRACT TRUNCATED AT 250 WORDS)

Model adducts of benzo[a]pyrene and nucleosides formed from its radical cation and diol epoxide

Reference adducts formed by reaction of deoxyribonucleosides with the ultimate carcinogenic forms of benzo[a]pyrene (BP), BP radical cation and BP diol epoxide, are essential for identifying the structures of adducts formed in biological systems. Electrochemical oxidation of BP in the presence of dG or dA produces adducts from BP radical cation. When 8 equiv of charge are consumed, four adducts are formed with dG: 7-(BP-6-yl)Gua, 8-(BP-6-yl)Gua, N2-(BP-6-yl)dG and 3-(BP-6-yl)dG. With 2 equiv of charge, however, only 7-(BP-6-yl)Gua and 8-(BP-6-yl)dG (BP-6-C8dG) are formed. Anodic oxidation of BP-6-C8dG affords 8-(BP-6-yl)Gua. Anodic oxidation of BP in the presence of dA produces 7-(BP-6-yl)Ade. Reaction of BP diol epoxide with dG yields 10-(guanin-7-yl)-7,8,9-trihydroxy-7,8,9,10-tetrahydroBP, whereas reaction with dA affords three adducts, 10-(adenin-7-yl)-7,8,9-trihydroxy-7,8,9,10-tetrahydroBP and two isomers of 10-(deoxyadenosin-N6-yl)-7,8,9-trihydroxy-7,8,9,10-tetrahydroBP . On the basis of comparative kinetic studies among adducts of aromatic hydrocarbons and dG or G, only BP-6-C8dG easily loses the sugar moiety, providing a basis for a mechanism of hydrolysis of the glycosidic bond.

Mechanism of metabolic activation of the potent carcinogen 7,12-dimethylbenz[a]anthracene

The DNA adducts of 7,12-dimethylbenz[a]anthracene (DMBA) previously identified in vitro and in vivo are stable adducts formed by reaction of the bay-region diol epoxides of DMBA with dG and dA. In this paper we report identification of several new DMBA-DNA adducts formed by one-electron oxidation, including two adducts lost from DNA by depurination, DMBA bound at the 12-methyl to the N-7 of adenine (Ade) or guanine (Gua) [7-methylbenz[a]anthracene (MBA-12-CH2-N7Ade or 7-MBA-12-CH2-N7Gua, respectively]. The in vitro systems used to study DNA adduct formation were DMBA activated by horseradish peroxidase or 3-methyl-cholanthrene-induced rat liver microsomes. The biologically-formed depurination adducts were identified by high-pressure liquid chromatography and by fluorescence line narrowing spectroscopy. Stable DMBA-DNA adducts were analyzed by the 32P-postlabeling method. Quantitation of DMBA-DNA adducts formed by microsomes showed about 99% as depurination adducts: 7-MBA-12-CH2-N7Ade (82%) and 7-MBA-12-CH2-N7Gua (17%). Stable adducts (1.4% of total) included one adduct spot that may contain adduct(s) formed from the diol epoxide (0.2%) and unidentified adducts (1.2%). Activation of DMBA by horseradish peroxidase afforded 56% of stable unidentified adducts and 44% of depurination adducts, with 36% of 7-MBA-12-CH2-N7Ade and 8% of 7-MBA-12-CH2-N7Gua. Adducts containing the bond to the DNA base at the 7-CH3 group of DMBA were not detected.(ABSTRACT TRUNCATED AT 250 WORDS)

The approach to understanding aromatic hydrocarbon carcinogenesis. The central role of radical cations in metabolic activation

Polycyclic aromatic hydrocarbons (PAH) are carcinogens requiring metabolic activation to react with cellular macromolecules, the initial event in carcinogenesis. Cytochrome P450 mediates binding of PAH to DNA by two pathways of activation. One-electron oxidation to form radical cations is the major pathway of activation for the most potent carcinogenic PAH, whereas monooxygenation to form bay-region diol epoxides is generally a minor pathway. For benzo[a]pyrene and 7,12-dimethylbenz[a]-anthracene, 80% and 99%, respectively, of the DNA adducts formed by rat liver microsomes or in mouse skin arise via the radical cation. Therefore, studies of PAH activation should begin by considering one-electron oxidation as the primary mechanism.

Comparative dose-response tumorigenicity studies of dibenzo[alpha,l]pyrene versus 7,12-dimethylbenz[alpha]anthracene, benzo[alpha]pyrene and two dibenzo[alpha,l]pyrene dihydrodiols in mouse skin and rat mammary gland

Comparative studies were conducted of the tumor-initiating activity in mouse skin and carcinogenicity in rat mammary gland of dibenzo[a,l]pyrene (DB[a,l]P) versus 7,12-dimethyl-benz[a]anthracene (DMBA), the most potent recognized carcinogenic polycyclic aromatic hydrocarbon (PAH); benzo[a]pyrene (B[a]P), the most potent recognized carcinogenic environmental PAH; DB[a,l]P 8,9-dihydrodiol, the K-region dihydrodiol; and DB[a,l]P 11,12-dihydrodiol, precursor to the bay-region diolepoxide. The tumor-initiating activity of DB[a,l]P and B[a]P was compared in the skin of female SENCAR mice at doses of 300, 100 and 33.3 nmol. The mice were promoted with 12-O-tetradecanoylphorbol-13-acetate (TPA) twice-weekly for 13 weeks. DB[a,l]P at all doses induced significantly more tumors than B[a]P at the corresponding dose, with a significantly shorter latency. Subsequently, the tumor-initiating activity of DB[a,l]P was compared in the skin of female SENCAR mice to that of DMBA, B[a]P, DB[a,l]P 8,9-dihydrodiol and DB[a,l]P 11,12-dihydrodiol at doses of 100, 20 and 4 nmol. The mice were promoted with TPA twice-weekly for 24 weeks. In addition, groups of mice were initiated with 100 nmol of DB[a,l]P, DMBA, B[a]P, DB[a,l]P 8,9-dihydrodiol or DB[a,l]P 11,12-dihydrodiol and kept without promotion. This experiment showed that in the mouse skin, DB[a,l]P and DB[a,l]P 11,12-dihydrodiol displayed similar tumor-initiating activity with a response inversely proportional to the dose, presumably due to the toxicity of the compounds. At the high dose they elicited tumors earlier than DMBA, though DMBA produced a much higher tumor multiplicity. At the low dose, DMBA, DB[a,l]P and DB[a,l]P 11,12-dihydrodiol exhibited similar tumorigenicities. DB[a,l]P 8,9-dihydrodiol was a marginal tumor initiator. Once again, DB[a,l]P was by far a much stronger tumor initiator than B[a]P. Female Sprague-Dawley rats were treated with 1.0 or 0.25 mumol of DB[a,l]P, DMBA or B[a]P by intramammillary injection at eight teats. DB[a,l]P at both doses was a more potent carcinogen than DMBA at the corresponding dose in the rat mammary gland. B[a]P was a marginal mammary carcinogen, eliciting only a few fibrosarcomas. Thus, these data suggest that DB[a,l]P is the strongest PAH carcinogen ever tested.

A monoclonal antibody to rat liver cytochrome P450 IIC11 strongly and regiospecifically inhibits constitutive benzo[a]pyrene metabolism and DNA binding

The monoclonal antibody MAb 1-68-11, prepared to constitutive cytochrome P450 IIC11 (2c/RLM5) from male Sprague-Dawley rat liver, was used to study the contribution of the class of cytochrome P450s epitopically related to P450 IIC11 to the regiospecific metabolism of benzo[a]pyrene (BP) and its binding to DNA. The effect of MAb 1-68-11 was determined on the conversion of BP to BP-9,10-dihydrodiol, BP-7,8-dihydrodiol, BP-4,5-dihydrodiol, BP phenols, and BP quinones, and on the P450-dependent DNA binding catalyzed by P450 in microsomes from uninduced male and female Wistar and Sprague-Dawley rat livers, as well as 3-methylcholanthrene- and phenobarbital (PB)-induced male Wistar rat livers. In liver microsomes from untreated male rats, MAb 1-68-11 inhibited BP-9,10-dihydrodiol formation by 80%; in liver microsomes from untreated female rats, the inhibition was 100%. BP-7,8-dihydrodiol formation was inhibited from 38 to 77% in microsomes from males and 50% in those from females. In microsomes from PB-induced rats, inhibition of the 9,10-dihydrodiol and the 7,8-dihydrodiol was 90% and 73%, respectively, whereas BP-4,5-dihydrodiol formation was enhanced 80%. In microsomes from 3-methylcholanthrene-treated rats, no inhibition of MAb 1-68-11 was observed on either the metabolism of BP or its binding to DNA. In contrast, the binding of BP to DNA was completely inhibited by MAb 1-68-11 in microsomes from uninduced male Wistar rats and 70% in PB-induced microsomes. 32P-postlabeling analysis showed that formation of the major stable adduct, BP diol epoxide bound at C-10 to the 2-amino of deoxyguanosine, was strongly inhibited in uninduced and PB-induced microsomes. Formation of the major labile BP-DNA adduct 7-(benzo[a]pyren-6-yl) guanine (BP-N7Gua) was inhibited about 60% in microsomes from untreated male Wistar rats. These results show that MAb 1-68-11 regiospecifically inhibits cytochrome P450 IIC11 and epitopically related P450s that metabolize BP at the 7,8 and 9,10 positions. MAb 1-68-11 also inhibits enzyme-catalyzed binding of BP to DNA in the specific formation of BP-N7Gua and adducts detected by the 32P-postlabeling technique.

Formation of 8-methylguanine as a result of DNA alkylation by methyl radicals generated during horseradish peroxidase-catalyzed oxidation of methylhydrazine

Methylhydrazine oxidation promoted by horseradish peroxidase-H2O2 or ferricyanide led to the generation of high yields of methyl radicals and to the formation of 7-methylguanine and 8-methylguanine upon interaction with calf thymus DNA. Methyl radicals were identified by spin-trapping experiments with alpha-(4-pyridyl-1-oxide)-N-tert-butyl nitrone and tert-nitrosobutane. The methylated guanine products were identified in the neutral hydrolysates of treated DNA by high pressure liquid chromatography (HPLC) analysis and spiking with authentic samples. The structure of 8-methylguanine, a product not previously reported in enzymatic systems, was confirmed by HPLC chromatography, UV absorbance, and mass spectrometry. The formation of 8-methylguanine suggests a possible role for carbon-centered radicals as DNA-alkylating agents.

Metabolism and mutagenicity of dibenzo[a,e]pyrene and the very potent environmental carcinogen dibenzo[a,l]pyrene

Dibenzo[a,l]pyrene (DB[a,l]P) is one of the most potent carcinogens ever tested in mouse skin and rat mammary gland. DB[a,l]P is present in cigarette smoke and, presumably, in other environmental pollutants. Metabolism and mutagenicity studies of this compound compared to the weak carcinogen dibenzo[a,e]pyrene (DB[a,e]P) can provide preliminary evidence on its mechanism of carcinogenesis. The mutagenicity of DB[a,l]P, DB[a,e]P, and benzo[a]pyrene (BP) was compared in the Ames assay with Aroclor-induced rat liver S-9. BP was the strongest mutagen. In strain TA100, DB[a,l]P and DB[a,e]P were marginally mutagenic. In strain TA98 both compounds were mutagenic, and DB[a,l]P induced more than twice as many revertants as DB[a,e]P. The mutagenicity of DB[a,l]P does not correlate with its carcinogenicity, since DB[a,l]P is a much stronger carcinogen, but a much weaker mutagen, than BP. The NADPH-supported metabolism of DB[a,e]P and DB[a,l]P was conducted with uninduced and 3-methylcholanthrene-induced rat liver microsomes. Metabolites were analyzed by reverse-phase HPLC and identified by NMR, UV, and mass spectrometry. Uninduced microsomes produced only traces of metabolites with either compound. The major metabolites of DB[a,l]P with induced microsomes were DB[a,l]P 8,9-dihydrodiol, DB[a,l]P 11,12-dihydrodiol, 7-hydroxyDB[a,l]P, and a DB[a,l]P dione. The metabolites of DB[a,e]P with induced microsomes were DB[a,e]P 3,4-dihydrodiol, 3-hydroxyDB[a,e]P, 7-hydroxyDB[a,e]P, and 9-hydroxyDB[a,e]P. Some of these metabolites are very useful in assessing possible pathways of activation in the initiation of cancer.

Identification and quantitation of 7-(benzo[a]pyren-6-yl)guanine in the urine and feces of rats treated with benzo[a]pyrene

The major identified benzo[a]pyrene (BP)-DNA adduct formed by cytochrome P-450 contains BP bound at the C-6 position to the N-7 position of guanine (BP-N7Gua). This adduct is rapidly depurinated from DNA. When rats were treated with [14C]BP, about 0.02% of the administered dose of BP was excreted as BP-N7Gua in feces and urine within 5 days. Chloroform extracts of the urine and feces were analyzed by high-pressure liquid chromatography. The structure of the adduct was established by cochromatography with electrochemically prepared BP-N7Gua and by fluorescence line narrowing spectrometry. This study represents the first demonstration that BP-N7Gua is formed in vivo in animals treated with BP.

Binding of benzo[a]pyrene to DNA by cytochrome P-450 catalyzed one-electron oxidation in rat liver microsomes and nuclei

To investigate whether cytochrome P-450 catalyzes the covalent binding of substrates to DNA by one-electron oxidation, the ability of both uninduced and 3-methylcholanthrene (MC) induced rat liver microsomes and nuclei to catalyze covalent binding of benzo[a]pyrene (BP) to DNA and formation of the labile adduct 7-(benzo[a]pyren-6-yl)guanine (BP-N7Gua) was investigated. This adduct arises from the reaction of the BP radical cation at C-6 with the nucleophilic N-7 of the guanine moiety. In the various systems studied, 1-9 times more BP-N7Gua adduct was isolated than the total amount of stable BP adducts in the DNA. The specific cytochrome P-450 inhibitor 2-[(4,6-dichloro-o-biphenyl)oxy]ethylamine hydrobromide (DPEA) reduced or eliminated BP metabolism, binding of BP to DNA, and formation of BP-N7Gua by cytochrome P-450 in both microsomes and nuclei. The effects of the antioxidants cysteine, glutathione, and p-methoxythiophenol were also investigated. Although cysteine had no effect on the microsome-catalyzed processes, glutathione and p-methoxythiophenol inhibited BP metabolism, binding of BP to DNA, and formation of BP-N7Gua by cytochrome P-450 in both microsomes and nuclei. The decreased levels of binding of BP to DNA in the presence of glutathione or p-methoxythiophenol are matched by decreased amounts of BP-N7Gua adduct and of stable BP-DNA adducts detected by the 32P-postlabeling technique. This study represents the first demonstration of cytochrome P-450 mediating covalent binding of substrates to DNA via one-electron oxidation and suggests that this enzyme can catalyze peroxidase-type electron-transfer reactions.

Radical cations in aromatic hydrocarbon carcinogenesis

Most carcinogens, including polycyclic aromatic hydrocarbons (PAH), require metabolic activation to produce the ultimate electrophilic species that bind covalently with cellular macromolecules to trigger the cancer process. Metabolic activation of PAH can be understood in terms of two main pathways: one-electron oxidation to yield reactive intermediate radical cations and monooxygenation to produce bay-region diol epoxides. The reason we have postulated that one-electron oxidation plays an important role in the activation of PAH derives from certain common characteristics of the radical cation chemistry of the most potent carcinogenic PAH. Two main features common to these PAH are: 1) a relatively low ionization potential, which allows easy metabolic removal of one electron, and 2) charge localization in the PAH radical cation that renders this intermediate specifically and efficiently reactive toward nucleophiles. Equally important, cytochrome P-450 and mammalian peroxidases catalyze one-electron oxidation. This mechanism plays a role in the binding of PAH to DNA. Chemical, biochemical and biological evidence will be presented supporting the important role of one-electron oxidation in the activation of PAH leading to initiation of cancer.

32P-postlabeling analysis of benzo[a]pyrene-DNA adducts formed in vitro and in vivo

Benzo[a]pyrene (BP) was bound to DNA by horseradish peroxidase, rat liver microsomes, and rat liver nuclei in vitro and in mouse skin in vivo. The BP-DNA adducts formed were analyzed by the 32P-postlabeling technique. Activation by microsomes and nuclei resulted in the detection of five adducts, including a major adduct (55%) which cochromatographed with the adduct (+/-)-10 beta-deoxyguanosin-N2-yl-7 beta, 8 alpha, 9 alpha-trihydroxy-7,8,9,10-tetrahydro-BP (BPDE-N2dG) formed by reaction of (+/-)-7 beta, 8 alpha-dihydroxy-9 alpha, 10 alpha-epoxy-7,8,9,10-tetrahydro-BP (BPDE) with DNA or by microsomal activation of BP 7,8-dihydrodiol. Activation by horseradish peroxidase, which catalyzes one-electron oxidation, produced seven adducts, including a major one (30%) that coeluted with an adduct observed with microsomal (2%) and nuclear (14%) activation. The pattern of adducts formed in mouse skin treated with BP in vivo for 4 or 24 h contained four of the same adducts observed with nuclei or microsomes in vitro, and the predominant adduct detected (86%) was BPDE-N2dG. The adduct common to horseradish peroxidase, microsomes, and nuclei was also detected in mouse skin DNA (2%). These results demonstrate that multiple BP-DNA adducts are formed in these in vitro and in vivo systems and suggest that at least one adduct is formed in common in all of the systems. Thus, it appears that stable BP adducts can be formed in mouse skin DNA by both monooxygenation and one-electron oxidation.

Tumor-initiating activity in mouse skin and carcinogenicity in rat mammary gland of dibenzo[a]pyrenes: the very potent environmental carcinogen dibenzo[a, l]pyrene

Comparative studies of tumor-initiating activity in mouse skin and carcinogenicity in rat mammary gland were conducted with several dibenzo[a]-pyrenes (DBPs). SENCAR mice were initiated with DB[a, e]P, DB[a, h]P, DB[a, i]P, DB[a, l]P and anthanthrene, and promoted with tetradecanoyl-phorbol acetate. The same compounds were tested by intramammillary injection in female Sprague-Dawley rats. Anthanthrene was inactive in both mouse skin and rat mammary gland. DB[a, e]P was a very weak tumor-initiator in mouse skin and was inactive in rat mammary gland. DB[a, h]P induced twice as many papillomas in mouse skin as DB[a, i]P, although both compounds exhibited similar tumor latencies and percentages of tumor-bearing mice. These two compounds induced similar numbers of mammary tumors, but treatment of the rats with DB[a, i]P resulted in a significantly larger number of adenocarcinomas. DB[a, l]P was toxic to both the mice and rats. Treatment of mouse skin with this compound led to an erythema, which delayed the beginning of promotion until the 3rd week after initiation. Despite this delay, papillomas began appearing 5 weeks after initiation with DB[a, l]P and the number of tumors increased rapidly. The compound was so toxic in the rats that half of the animals died in the first 9 weeks and the remaining animals were sacrificed after 15 weeks. Nonetheless, DB[a, l]P was the strongest carcinogen tested, inducing seven tumors per rat within 10 weeks. These results demonstrate that DB[a, l]P, which is present in tobacco smoke, is an extremely potent carcinogenic aromatic hydrocarbon. Furthermore, some of these compounds can serve as useful models for elucidating their mechanisms of activation.

Fluorescence line narrowing spectrometric analysis of benzo[a]pyrene-DNA adducts formed by one-electron oxidation

Fluorescence line narrowing (FLN) was demonstrated for five benzo[a]pyrene (BP)-nucleoside adducts synthesized by one-electron oxidation of BP in the presence of guanosine, deoxyguanosine, and deoxyadenosine. The standard FLN spectra were used to prove that a major depurination adduct from the binding of BP to DNA in rat liver nuclei is 7-(benzo[a]pyren-6-yl)guanine (N7Gua). The structural characterization was performed with only 20 pg of the adduct. Metabolic activation of BP by one-electron oxidation in the horseradish peroxidase catalyzed reaction of BP with DNA (in vitro) was also investigated. The major adduct identified was 8-(benzo[a]pyren-6-yl)guanine (C8Gua).

Radical cations in the horseradish peroxidase and prostaglandin H synthase mediated metabolism and binding of benzo[a]pyrene to deoxyribonucleic acid

Metabolism and DNA binding studies are used to investigate mechanisms of activation for carcinogens. In this paper we describe metabolism of benzo[a]pyrene (BP) and 6-fluorobenzo[a]pyrene (6-FBP) by two peroxidases, horseradish peroxidase (HRP) and prostaglandin H synthase (PHS), which are known to catalyze one-electron oxidation. In addition, binding of BP and BP quinones to DNA was compared in the two enzyme systems. The only metabolites formed from BP or 6-FBP by either enzyme were the quinones, BP 1,6-, 3,6- and 6,12-dione. HRP metabolized BP and 6-FBP to the same extent and produced the same proportion of each dione from both compounds, approximately 40% each of BP 1,6- and 3,6-dione and 20% BP 6,12-dione. PHS formed twice as much quinones from BP as from 6-FBP and produced relatively more BP 3,6-dione from 6-FBP (46%) compared to BP (30%) and relatively less BP 6,12-dione from 6-FBP (16%) compared to BP (33%). Removal of the fluoro substituent in the metabolism of 6-FBP is consistent only with an initial one-electron oxidation of the substrate. Since BP quinones were the only products formed in HRP- and PHS-catalyzed activation of BP, their possible binding to DNA was compared to that of BP. No significant binding of BP quinones to DNA occurred with either HRP or PHS. These results, coupled with those from other chemical and biochemical experiments, demonstrate that HRP- and PHS-catalyzed one-electron oxidation of BP to its radical cation is the mechanism of formation of quinones and binding of BP to DNA.

Radical cations as precursors in the metabolic formation of quinones from benzo[a]pyrene and 6-fluorobenzo[a]pyrene. Fluoro substitution as a probe for one-electron oxidation in aromatic substrates

Three classes of products are formed when benzo[a]pyrene (BP) is metabolized by cytochrome P-450: dihydrodiols, phenols and the quinones, BP 1,6-, 3,6- and 6,12-dione. These products have been thought to arise from attack of a catalytically-activated electrophilic oxygen atom. In this paper we report chemical and biochemical experiments which demonstrate that BP quinones arise from an initial one-electron oxidation of BP to form its radical cation. BP, 6-fluorobenzo[a]pyrene (6-FBP), 6-chlorobenzo[a]pyrene (6-ClBP), and 6-bromobenzo[a]pyrene (6-BrBP) were metabolized by uninduced and 3-methylcholanthrene-induced rat liver microsomes in the presence of NADPH or cumene hydroperoxide (CHP) as cofactor. BP and 6-FBP produced similar metabolic profiles with induced microsomes in the presence of NADPH or 2 mM CHP. With NADPH both compounds produced dihydrodiols, phenols and quinones, whereas with CHP, they yielded only quinones. Metabolism of BP and 6-FBP was also similar with uninduced microsomes and 2 mM CHP, yielding the same BP quinones. With uninduced microsomes in the presence of NADPH, BP produced all three classes of metabolites, whereas 6-FBP afforded only quinones. At a low concentration of CHP (0.10 mM), BP was metabolized to phenols and quinones, whereas 6-FBP gave only quinones. 6-ClBP and 6-BrBP were poor substrates, forming metabolites only with induced microsomes and NADPH. One-electron oxidation of BP by Mn(OAc)3 occurred exclusively at C-6 with predominant formation of 6-acetoxyBP and small amounts of BP quinones. In the one-electron oxidation of 6-FBP by Mn(OAc)3, the major products obtained were 6-acetoxyBP, a mixture of 1,6- and 3,6-diacetoxyBP, and BP quinones. Reaction of BP and 6-FBP radical cation perchlorates with water produced the same BP quinones. Conversely, electrophilic substitution of 6-FBP with bromine or deuterium ion afforded C-1 and/or C-3 derivatives with retention of the fluoro substituent at C-6. These results indicate that metabolic formation of BP quinones from BP and 6-FBP can only derive from their intermediate radical cation.

Mutagenicity of benzylic acetates, sulfates and bromides of polycyclic aromatic hydrocarbons

Studies were performed to determine the direct mutagenicity of the acetates and some bromides and sulfates of hydroxymethyl polycyclic aromatic hydrocarbons in S. typhimurium strains TA98 and TA100. Benzylic acetates, bromides and sulfates were synthesized and characterized. The compounds tested were benzyl alcohol, 5-hydroxymethylchrysene, 1-hydroxymethylpyrene, 6-hydroxymethylbenzo[a]pyrene, 6-(2-hydroxyethyl)benzo[a]pyrene, 6-hydroxymethylanthanthrene, 9-hydroxymethylanthracene, 9-hydroxymethyl-10-methylanthracene, 7-hydroxymethylbenz[a]anthracene, 7-(2-hydroxyethyl)benz[a]anthracene, 12-hydroxymethylbenz[a]anthracene, 7-hydroxymethyl-12-methylbenz[a]anthracene, 12-hydroxymethyl-7-methylbenz[a]anthracene, 1-hydroxy-3-methylcholanthrene, 2-hydroxy-3-methylcholanthrene, 3-hydroxy-3, 4-dihydrocyclopental[cd]pyrene and 4-hydroxy-3, 4-dihydrocyclopental[cd]pyrene. The benzylic sulfate esters of 6-hydroxymethylbenzo[a]pyrene and 7-hydroxymethylbenz[a]anthracene were the most mutagenic compounds, whereas the aliphatic sulfate ester of 7-hydroxyethylbenz[a]anthracene did not cause an increase in mutations above background. All meso-anthracenic benzylic acetate esters were mutagenic in both strains with various degrees of activity, whereas the corresponding non-benzylic esters were inactive, as expected. Of the non-meso-benzylic acetate esters, only the 3-acetoxy-3, 4-dihydrocyclopenta[cd]pyrene was mutagenic. In the benzylic bromide series, only the eight mesoanthracenic were mutagenic, whereas benzyl bromide and 5-bromomethylchrysene were inactive. The aliphatic bromides, 6-(2-bromoethyl)benzo[a]pyrene and 7-(2-bromoethyl)benz[a]anthracene did not display significant activity. The potencies of the acetate esters more accurately reflect the mutagenicity because the rate of solvolysis did not compete with the reactivity of the esters with bacterial DNA. In the case of benzylic sulfates and bromides, the rate of solvolysis was very rapid and could have diminished the level of mutagenicity, depending on the assay conditions. These results demonstrate that meso-anthracenic benzylic acetates, sulfates and bromides are mutagenic, whereas benzylic acetate esters attached to other carbon atoms are inactive.

Mutagenicity of selected functionalized benz(c)acridines and a benz(a)phenazine in the Salmonella typhimurium/microsome assay

Five functionalized benz(c)acridines - 5,6-dimethylbenz(c)acridine; 5,6,7-trimethylbenz(c)acridine; 7-chloro-5,6-dimethylbenz(c)acridine; 7-amino-5,6-dimethylbenz(c)acridine; 7-oxo-5,6-dimethylbenz(c)-acridine and 5,6-dimethylbenz(a)phenazine - were tested for mutagenic activity in the Ames Salmonella typhimurium assay. Compounds were initially screened by spot tests with 5 tester strains and both plate incorporation and pre-incubation assays were performed when the results of the tests were positive or weakly positive. All assays were done with and without S9 activation. 7-Amino-5, 6-dimethylbenz(c)acridine and 7-chloro-5, 6-dimethylbenz(c)acridine were found to be moderately mutagenic with the 3 frameshift strains TA1537, TA98, and TA97.

Structure elucidation of a 6-methylbenzo[a]pyrene-DNA adduct formed by horseradish peroxidase in vitro and mouse skin in vivo

Activation of polycyclic aromatic hydrocarbons (PAH) by horseradish peroxidase (HRP) with H2O2 has been studied as a model system for one-electron oxidation. This peroxidase has been used to catalyze binding of 6-[14C]methylbenzo[a]pyrene (BP-6-CH3) to DNA, which was purified, hydrolyzed to deoxyribonucleosides and analyzed by high pressure liquid chromatography (HPLC). The predominant hydrocarbon-DNA adduct observed was identified as BP-6-CH3 bound at the 6-methyl group to the 2-amino group of dG, confirming that activation by HRP occurs by one-electron oxidation. When DNA from mouse skin treated in vivo with [14C]BP-6-CH3 was purified, hydrolyzed and analyzed by HPLC, a profile was observed which was qualitatively similar to that from the peroxidase system. In particular, the identified adduct with the hydrocarbon bound at the 6-methyl group to the 2-amino group of dG was obtained. These results demonstrate that one-electron oxidation is the mechanism of activation by HRP for aromatic hydrocarbons and indicate that the same mechanism may occur in mouse skin, a target tissue for hydrocarbon carcinogenesis.

The relationship between ionization potential and horseradish peroxidase/hydrogen peroxide-catalyzed binding of aromatic hydrocarbons to DNA

The ionization potentials (IP) of 91 alternant polycyclic aromatic hydrocarbons (PAH) were determined from the absorption maximum of the charge-transfer complex of each hydrocarbon and chloranil in chloroform. The extent of horseradish peroxidase (HRP)-catalyzed binding to DNA of 14 hydrocarbons of varying IP was measured. Only hydrocarbons with IP less than approx. 7.35 eV were significantly bound to DNA. These results provide further evidence that HRP-mediated binding of PAH to DNA occurs by one-electron oxidation and indicate that hydrocarbons must have IP less than approx. 7.35 eV to be activated by one-electron oxidation. Thus, determination of IP and HRP-catalyzed binding to DNA can offer some guidelines for selecting aromatic hydrocarbons which might undergo carcinogenic activation by this mechanism.

Microbial mutagenicity of selected hydrazines

Selected hydrazines and related compounds were examined for their mutagenic activity in S. typhimurium strains TA1535 and TA1537. These in vitro assays were conducted with and without metabolic activation by Aroclor-induced rat-liver enzymes. Relatively high levels of mutagenicity were observed with phenylhydrazine X HCl, methylhydrazine, N'-acetyl-4-(hydroxymethyl)phenylhydrazine, and 4-(hydroxymethyl)benzenediazonium tetrafluoroborate, the stabilized salt of a carcinogenic metabolite of agaritine; only low levels of mutagenicity were observed with other compounds, although most are strong carcinogens. Several of the compounds were highly toxic to the bacteria, and detection of mutagenicity was enhanced by calculating the increase in mutagenic activity on the basis of the surviving fractions of bacteria.

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.

Metabolic activation of aromatic hydrocarbons in purified rat liver nuclei: induction of enzyme activities and binding to DNA with and without monooxygenase-catalyzed formation of active oxygen

Purified rat liver nuclei covalently bound low levels of seven aromatic [14C]hydrocarbons to nuclear DNA. Induction with 3-methylcholanthrene increased the binding of six carcinogenic hydorcarbons, but did not raise the level of binding of noncarcinogenic anthracence. Removal of the nuclear envelope by Triton N-101 eliminated binding and aryl hydrocarbon hydroxylase activities and cytochrome P-450 from the nuclei. Binding of two of two strong carcinogens, benzo[a]pyrene and 7,12-dimethylbenz[a]anthracene, to nuclear DNA was compared to the levels of aryl hydrocarbon hydroxylase and cytochrome P-450 in nuclei from uninduced and benz[a]anthracene-, 3-methylcholanthrene-, and phenobarbital-induced rats. Microsomal hydroxylase and cytochrome P-450 were also assayed. Induction with 3-methylcholanthrene gave the largest increases in nuclear activities: 11 times as much hydroxylase, 6 times as much cytochrome P-450, and 4 times as much binding of both hydrocarbons. Benz[a]anthracene and phenobarbital induced these nuclear activities 0- to 4-fold. In the presence of added NADPH, binding of benzol[a]pyrene to DNA by nuclei increased rapidly for at least 20 min. When NADPH was not added, the reaction stopped at a low level in 5 min. When CO was bubbled through the reaction mixture with or without added NADPH, binding of benzo[a]pyrene and 7,12-dimethylbenz[a]anthracene was partially inhibited, indicating that cytochrome P-450 plays a role in this activation. Since no nuclear hydroxylase activity was seen without added NADPH or in the presence of CO, activation and subsequent binding of hydrocarbons to nuclear DNA, at least in part, does not require the activated oxygen used in monooxygenase reactions.

Studies on the pathway of incorporation of 2-aminopurine into the deoxyribonucleic acid of Escherichia coli

A pathway for the incorporation of 2-aminopurine into deoxyribonucleic acid (DNA) was studied in cell-free extracts of Escherichia coli. It was demonstrated that the free base can be converted to the deoxynucleoside, and that the deoxynucleotide can be phosphorylated to the di- and triphosphates and then incorporated into the DNA. From a consideration of the individual reactions in crude extracts, it is likely that the rate-limiting step in this pathway is the formation of the deoxynucleotide. Of especial interest is the observation that 2-aminopurine may be viewed as an analogue of either guanine or adenine, depending on which enzymatic step is being considered. On the one hand, it resembles guanine in that it is specifically converted from the mono- to the diphosphate by guanylate kinase and not by adenylate kinase. On the other hand, it replaces adenine rather than guanine in the DNA synthesized with purified DNA polymerases. E. coli DNA polymerase utilizes aminopurine deoxynucleoside triphosphate as a substrate for DNA synthesis much better than does purified phage T5-induced DNA polymerase and is also much less inhibited by this analogue than the T5 enzyme. These experiments in vitro correlate with known differential effects of 2-aminopurine on E. coli and phage in vivo.