Formation and persistence of DNA adducts formed by the carcinogenic air pollutant 3-nitrobenzanthrone in target and non-target organs after intratracheal instillation in rats.

Sprague-Dawley rats were treated by intratracheal instillation with a single dose of 0.2 mg/kg body wt of 3-nitrobenzanthrone (3-NBA), and whole blood, lungs, pancreases, kidneys, urinary bladders, hearts, small intestines and livers were removed at various times after administration. At five posttreatment times (2 days, 2, 10, 20 and 36 weeks), DNA adducts were analysed in each tissue by (32)P-postlabelling to study their long-term persistence. 3-NBA-derived DNA adducts consisting of the same adduct pattern were observed in all tissues from animals killed between 2 days and 36 weeks and between 2 days and 20 weeks in blood. DNA isolated from whole blood contained the same 3-NBA-specific adduct pattern as that found in tissues. Although total adduct levels in the blood were much lower than those found in the lung, the target organ of 3-NBA tumourigenicity, they were related (20-25%, R(2) = 0.98) to the levels found in lung. In all organs, total adduct levels decreased over time to 20-30% of the initial levels till the latest time point (36 weeks) and showed a biphasic profile, with a rapid loss during the first 2 weeks followed by a much slower decline that reached a stable plateau at 20 weeks after treatment. These results show that uptake of 3-NBA by the lung induces high levels of specific DNA adducts in target and non-target organs of the rat. The correlation between DNA adducts in lung and blood suggests that persistent 3-NBA-DNA adducts in the blood may be useful biomarkers for human respiratory exposure to 3-NBA.

Synthesis, characterization, and 32p-postlabeling analysis of DNA adducts derived from the environmental contaminant 3-nitrobenzanthrone.

3-Nitrobenzanthrone (3-NBA) is a potent mutagen and potential human carcinogen identified in diesel exhaust and ambient air particulate matter. 3-NBA forms DNA adducts in rodent tissues that arise principally through reduction to N-hydroxy-3-aminobenzanthrone (N-OH-ABA), esterification to its acetate or sulfate ester, and reaction of this activated ester with DNA. We detected 3-NBA-derived DNA adducts in rodent tissues by (32)P-postlabeling and generated them chemically by acid-catalyzed reaction of N-OH-ABA with DNA, but their structural identification has not yet been reported. We have now prepared 3-NBA-derived adducts by reaction of a possible reactive metabolite, N-acetoxy-N-acetyl-3-aminobenzanthrone (N-Aco-N-Ac-ABA), with purine nucleosides and nucleotides, characterized them, and have shown that they are present in DNA treated with this 3-NBA derivative. Three of these adducts have been characterized as the C-C adduct N-acetyl-3-amino-2-(2'-deoxyguanosin-8-yl)benzanthrone, the C-N adduct N-acetyl-N-(2'-deoxyguanosin-8-yl)-3-aminobenzanthrone, and an unusual 3-acetylaminobenzanthrone adduct of deoxyadenosine, which involves a double linkage between adenine and benzanthrone (N1 to C1, N(6) to C11b), creating a five-membered imidazo type ring system. According to IUPAC fused ring conventions, we propose the following systematic name for this adduct: (9'-(2' '-deoxyribofuranosyl))purino[6',1':2,3]imidazo[5,4-p](1,11b-dihydro-(N-acetyl-3-amino))benzanthrone. The 3'-phosphates of these novel adducts could be 5'-postlabeled using [gamma-(32)P]ATP, although the efficiency of labeling was found to be low (less than 20%). However, none of these adducts could be detected in DNA from 3-NBA-treated rats by (32)P-postlabeling. Two of these synthetic adducts were treated with alkali to generate nonacetylated adducts, and these were also shown by HPLC to differ from those adducts found in rat DNA. Therefore, a different approach to the synthesis of authentic standards is needed for the structural characterization of 3-NBA-derived DNA adducts formed in vivo.

Environmental pollutant and potent mutagen 3-nitrobenzanthrone forms DNA adducts after reduction by NAD(P)H:quinone oxidoreductase and conjugation by acetyltransferases and sulfotransferases in human hepatic cytosols.

3-Nitrobenzanthrone (3-nitro-7H-benz[de]anthracen-7-one, 3-NBA) is a potent mutagen and suspected human carcinogen identified in diesel exhaust and air pollution. We compared the ability of human hepatic cytosolic samples to catalyze DNA adduct formation by 3-NBA. Using the (32)P-postlabeling method, we found that 12/12 hepatic cytosols activated 3-NBA to form multiple DNA adducts similar to those formed in vivo in rodents. By comparing 3-NBA-DNA adduct formation in the presence of cofactors of NAD(P)H:quinone oxidoreductase (NQO1) and xanthine oxidase, most of the reductive activation of 3-NBA in human hepatic cytosols was attributed to NQO1. Inhibition of adduct formation by dicoumarol, an NQO1 inhibitor, supported this finding and was confirmed with human recombinant NQO1. When cofactors of N,O-acetyltransferases (NAT) and sulfotransferases (SULT) were added to cytosolic samples, 3-NBA-DNA adduct formation increased 10- to 35-fold. Using human recombinant NQO1 and NATs or SULTs, we found that mainly NAT2, followed by SULT1A2, NAT1, and, to a lesser extent, SULT1A1 activate 3-NBA. We also evaluated the role of hepatic NADPH:cytochrome P450 oxidoreductase (POR) in the activation of 3-NBA in vivo by treating hepatic POR-null mice and wild-type littermates i.p. with 0.2 or 2 mg/kg body weight of 3-NBA. No difference in DNA binding was found in any tissue examined (liver, lung, kidney, bladder, and colon) between null and wild-type mice, indicating that 3-NBA is predominantly activated by cytosolic nitroreductases rather than microsomal POR. Collectively, these results show the role of human hepatic NQO1 to reduce 3-NBA to species being further activated by NATs and SULTs.

DNA adduct formation by the environmental contaminant 3-nitrobenzanthrone after intratracheal instillation in rats.

3-Nitrobenzanthrone (3-NBA) is an environmental pollutant and suspected human carcinogen found in emissions from diesel and gasoline engines and on the surface of ambient air particulate matter; human exposure to 3-NBA is likely to occur primarily via the respiratory tract. In our study female Sprague Dawley rats were treated by intratracheal instillation with a single dose of 0.2 or 2 mg/kg body weight of 3-NBA. Using the butanol enrichment version of the (32)P-postlabeling method, DNA adduct formation by 3-NBA 48 hr after intratracheal administration in different organs (lung, pancreas, kidney, urinary bladder, heart, small intestine and liver) and in blood was investigated. The same adduct pattern consisting of up to 5 DNA adduct spots was detected by thin layer chromatography in all tissues and blood and at both doses. Highest total adduct levels were found in lung and pancreas (350 +/- 139 and 620 +/- 370 adducts per 10(8) nucleotides for the high dose and 39 +/- 18 and 55 +/- 34 adducts per 10(8) nucleotides for the low dose, respectively) followed by kidney, urinary bladder, heart, small intestine and liver. Adduct levels were dose-dependent in all organs (approximately 10-fold difference between doses). It was demonstrated by high performance liquid chromatography (HPLC) that all 5 3-NBA-derived DNA adducts formed in rats after intratracheal instillation are identical to those formed by other routes of application and are, as previously shown, formed from reductive metabolites bound to purine bases. Although total adduct levels in the blood were much lower (41 +/- 27 and 9.5 +/- 1.9 adducts per 10(8) nucleotides for the high and low dose, respectively) than those found in the lung, they were related to dose and to the levels found in lung. These results show that uptake of 3-NBA by the lung induces high levels of specific DNA adducts in several organs of the rat and an identical adduct pattern in DNA from blood. Therefore, 3-NBA-DNA adducts present in the blood are useful biomarkers for exposure to 3-NBA and may help to assess the effective biological dose in humans exposed to it.

Identification of a genotoxic mechanism for 2-nitroanisole carcinogenicity and of its carcinogenic potential for humans.

2-Nitroanisole (2-NA) is an important industrial pollutant and a potent bladder carcinogen for rodents. The mechanism of its carcinogenicity was investigated in this study. Here we have used two independent methods, (32)P-post-labeling and (3)H-labeled 2-NA, to show that 2-NA binds covalently to DNA in vitro after reductive activation by human hepatic cytosol and xanthine oxidase (XO). We also investigated the capacity of 2-NA to form DNA adducts in vivo. Male Wistar rats were treated i.p. with 2-NA (0.15 mg/kg body wt daily for 5 days) and DNA from several organs was analyzed by (32)P-post-labeling. Two 2-NA-specific DNA adducts, identical to those found in DNA incubated with 2-NA and human hepatic cytosol or XO in vitro, were detected in the urinary bladder (3.4 adducts/10(7) nt), the target organ, and, to a lesser extent, in liver, kidney and spleen. The two DNA adducts found in rat tissues in vivo were identified as deoxyguanosine adducts derived from a 2-NA reductive metabolite, N-(2-methoxyphenyl)hydroxylamine. This reactive metabolite of 2-NA was identified in incubations with human hepatic cytosol, besides 2-methoxyaniline (o-anisidine). The results of our study, the first report on the potential of human cytosolic enzymes to contribute to the activation of 2-NA by nitroreduction, strongly suggest a carcinogenic potency of this rodent carcinogen for humans.

DNA adduct formation by the environmental contaminant 3-nitrobenzanthrone in V79 cells expressing human cytochrome P450 enzymes.

Diesel exhaust is known to induce tumours in animals. Of the compounds found in diesel exhaust 3-nitrobenzanthrone (3-NBA) is particularly a powerful mutagen. Recently we showed that 3-NBA is genotoxic in vivo in rats by forming specific DNA adducts derived from nitroreduction. In this study a panel of genetically engineered V79 Chinese hamster cell lines expressing various human cytochrome P450 (CYP) enzymes (CYP1A1, CYP3A4) and/or human NADPH:CYP oxidoreductase (CYPOR) was used to identify CYP enzymes involved in the metabolic activation of 3-NBA. We analyzed the formation of specific DNA adducts by 32P-postlabelling after exposing cells to 1 microM 3-NBA. A similar pattern with a total of four distinct 3-NBA-DNA adducts was found in all cells, identical to those detected previously in DNA from rats treated with 3-NBA in vivo. Total adduct levels ranged from 75 to 132 using nuclease P1 and from 103 to 220 adducts per 10(8) nucleotides, using butanol enrichment. Comparison of DNA binding between different V79MZ derived cells revealed that human CYPOR and CYP3A4 were involved in the metabolic activation of 3-NBA. Furthermore, dose-dependent high adduct levels were detected after exposure to 0.01, 0.1 or 1 microM 3-NBA in the subclone V79NH which exhibits high activities of nitroreductase and N,O-acetyltransferase. Our results suggest that nitroreduction is the major pathway in the human bioactivation of 3-NBA. Moreover, acetylation of the initially formed N-hydroxy arylamine intermediates may contribute to the high genotoxic potential of 3-NBA.

Covalent binding of the anticancer drug ellipticine to DNA in V79 cells transfected with human cytochrome P450 enzymes.

Ellipticine is a potent antineoplastic agent whose mechanism of action is considered to be based mainly on DNA intercalation and/or inhibition of topoisomerase II. Recently, we found that ellipticine also forms covalent DNA adducts and that the formation of the major adduct is dependent on the activation of ellipticine by cytochrome P450 (CYP). We examined a panel of genetically engineered V79 cell lines including the parental line V79MZ and recombinant cells expressing the human CYP enzymes CYP1A1, CYP1A2 or CYP3A4 for their ability to activate ellipticine. The extent of activation was determined by analysing DNA adducts by 32P-postlabelling. Ellipticine was found to be toxic to all V79 cell lines with IC(50) values ranging from 0.25 to 0.40 microM. The nuclease P1 version of the 32P-postlabelling assay yielded a similar pattern of ellipticine-DNA adducts with two major adducts in all cells, the formation of only one of which was dependent on CYP activity. This pattern is identical to that detected in DNA reacted with ellipticine and the reconstituted CYP enzyme system in vitro as confirmed by HPLC of the isolated adducts. Total adduct levels ranged from 2 to 337 adducts per 10(8) nucleotides, in the parental line and in V79 expressing CYP3A4, respectively. As in vitro, human CYP1A2 and CYP1A1 were less active. The results presented here are the first report showing the formation of CYP-mediated covalent DNA adducts by ellipticine in cells in culture, and confirm the formation of covalent DNA adducts as a new mechanism of ellipticine action.