The environmental pollutant and carcinogen 3-nitrobenzanthrone induces cytochrome P450 1A1 and NAD(P)H:quinone oxidoreductase in rat lung and kidney, thereby enhancing its own genotoxicity (original) (raw)
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Cancer Research, 2005
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,Oacetyltransferases (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. (Cancer Res 2005; 65(7): 2644-52) Note: V.M. Arlt and M. Stiborova contributed equally to this work. Requests for reprints: Volker M. Arlt, Section of Molecular Carcinogenesis,
International Journal of Cancer, 2006
3-Nitrobenzanthrone (3-NBA) is a potent mutagen and potential human carcinogen identified in diesel exhaust and ambient air particulate matter. Previously, we detected the formation of 3-NBAderived DNA adducts in rodent tissues by 32 P-postlabeling, all of which are derived from reductive metabolites of 3-NBA bound to purine bases, but structural identification of these adducts has not yet been reported. We have now prepared 3-NBA-derived DNA adduct standards for 32 P-postlabeling by reacting N-acetoxy-3-aminobenzanthrone (N-Aco-ABA) with purine nucleotides. Three deoxyguanosine (dG) adducts have been characterised as N-(2 0-deoxyguanosin-8-yl)-3-aminobenzanthrone-3 0-phosphate (dG3 0 p-C8-N-ABA), 2-(2 0-deoxyguanosin-N 2-yl)-3-aminobenzanthrone-3 0-phosphate (dG3 0 p-N 2-ABA) and 2-(2 0-deoxyguanosin-8-yl)-3-aminobenzanthrone-3 0-phosphate (dG3 0 p-C8-C2-ABA), and a deoxyadenosine (dA) adduct was characterised as 2-(2 0-deoxyadenosin-N 6-yl)-3aminobenzanthrone-3 0-phosphate (dA3 0 p-N 6-ABA). 3-NBA-derived DNA adducts formed experimentally in vivo and in vitro were compared with the chemically synthesised adducts. The major 3-NBA-derived DNA adduct formed in rat lung cochromatographed with dG3 0 p-N 2-ABA in two independent systems (thin layer and high-performance liquid chromatography). This is also the major adduct formed in tissue of rats or mice treated with 3-aminobenzanthrone (3-ABA), the major human metabolite of 3-NBA. Similarly, dG3 0 p-C8-N-ABA and dA3 0 p-N 6-ABA cochromatographed with two other adducts formed in various organs of rats or mice treated either with 3-NBA or 3-ABA, whereas dG3 0 p-C8-C2-ABA did not cochromatograph with any of the adducts found in vivo. Utilizing different enzymatic systems in vitro, including human hepatic microsomes and cytosols, and purified and recombinant enzymes, we found that a variety of enzymes [NAD(P)H:quinone oxidoreductase, xanthine oxidase, NADPH:cytochrome P450 oxidoreductase, cytochrome P450s 1A1 and 1A2, N,O-acetyltransferases 1 and 2, sulfotransferases 1A1 and 1A2, and myeloperoxidase] are able to catalyse the formation of 2-(2 0-deoxyguanosin-N 2-yl)-3-aminobenzanthrone, N-(2 0-deoxyguanosin-8-yl)-3-aminobenzanthrone and 2-(2 0-deoxyadenosin-N 6-yl)-3-aminobenzanthrone in DNA, after incubation with 3-NBA and/or 3-ABA.
Mutagenesis, 2007
The carcinogenic vehicle emission product 3-nitrobenzanthrone (3-NBA) is known to rearrange in the atmosphere to the isomer 2-nitrobenzanthrone (2-NBA), which exists in 70-fold higher concentration in ambient air. The genotoxicity of 2-NBA and 3-NBA was studied both in vitro (human cell lines A549 and HepG2) and in vivo (F344 female rats intra-tracheally administered 5 mg/kg body weight of 3-NBA) models, using the 32 P-HPLC and the single-cell gel electrophoresis (Comet assay) methods. In vitro, also the parent compound benzanthrone (BA) and the metabolite 3aminobenzanthrone (3-ABA) were evaluated. 3-NBA gave highest levels of DNA adducts in the two cell lines, but significantly higher in HepG2 (relative adduct level $ 500 adducts/10 8 normal nucleotides), whereas 2-NBA formed about one-third and one-twentieth of the DNA adduct amount in A549 and HepG2 cells, respectively. 3-ABA formed only minute amounts of DNA adducts and only in the A549 cells, whereas BA did not give rise to any detectable levels. The DNA adduct patterns from 3-NBA were similar between the two model systems, but differed somewhat for 2-NBA. The oxidative stress induced by BA was almost as high as what was observed for 3-NBA and 3-ABA in both cell lines, and 2-NBA induced lowest level of oxidative stress. The oxidative stress and DNA adduct level, in whole blood, was significantly increased by 3-NBA but not by 2-NBA. However, 2-NBA showed similar toxicity to 3-NBA, with respect to DNA adduct formation in vivo, hence it is important to further study 2-NBA as a potential contributor to health risk. While DNA adduct level in the 3-NBAexposed animals reached a peak around 1 and 2 days after instillation, 2-NBA-treated animals showed a tendency towards a continuing increase at the end of the study.
Carcinogenesis, 2006
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-NBAderived 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 5 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.
Environmental and Molecular Mutagenesis, 2006
3-Nitrobenzanthrone (3-NBA) is an urban air pollutant and rat lung carcinogen that is among the most potent mutagens yet tested in the Salmonella reversion assay. In the present study, 1 mg 3-NBA was administered orally to female F344 rats and DNA adduct formation was examined in liver, lung, kidney and five sections of the gastrointestinal (GI) tract at 6 hr, and 1, 2, 3, 5, and 10 days after administration. The DNA adduct patterns, analyzed by 32 P-postlabelling followed by HPLC separation, were similar in all tissues and organs. Five of the adduct peaks cochromatographed with synthesized DNA adduct standards. Three of these unequivocally determined standards, dGp-C8-N-ABA, dGp-N2-C2-ABA, and dAp-N6-C2-ABA, were of the nonacetylated type, suggesting that at least part of the pathway for activation of 3-NBA proceeds through O-acetylation of the hydroxylamine intermediate. The two other DNA adduct standards, dGp-C8-C2-N-Ac-ABA, and dGp-N2-C2-N-Ac-ABA, were of the acetylated type, but there was some ambiguity in the characterization of these DNA adducts, since they varied inconsistently between samples and they also aligned with peaks found in controls. At 6 hr after treatment, the level of DNA adducts was highest in glandular stomach (relative adduct labeling (RAL), *70 adducts/10 8 normal nucleotides (NN)); adduct levels in this organ decreased at 24 hr, but increased afterwards. DNA adduct levels in the majority of organs were characterized by an early increase (from 6 hr to 3 days), which was followed by a decrease at 5 days and a maximum level 10 days after administration (RAL *120 adducts/10 8 NN for the lung, kidney and glandular stomach, *80 adducts/10 8 NN for the forestomach and ceacum, and *40 adducts/10 8 NN for the liver, small intestine, and colon). This pattern was consistent with pathological observations during autopsy showing high levels of tissue damage in the GI tract; the tissue damage included hemorrhages, loss of villous surface structure in the small intestine, as well as intestine fragility and oedema of the adipose tissue around the GI-tract. Tissue damage decreased and DNA adduct levels increased at 10 days after administration. These observations suggest that 3-NBA not only exerts acute toxic effects, but that the bioavailability is affected by storage in tissues and later becomes available, resulting in the increased DNA adduct levels at the later time points of collection.
Mutagenicity and DNA Adduct Formation by the Urban Air Pollutant 2-Nitrobenzanthrone
Toxicological Sciences, 2007
2-Nitrobenzanthrone (2-NBA) has recently been detected in ambient air particulate matter. Its isomer 3-nitrobenzanthrone (3-NBA) is a potent mutagen and suspected human carcinogen identified in diesel exhaust. The highest mutagenic activity of 2-NBA tested in Salmonella typhimurium was exhibited in strain TA1538-hSULT1A1 expressing human sulfotransferase (SULT) 1A1. 2-NBA also induced mutations in Chinese hamster lung V79 cells expressing human N-acetyltransferase 2 or SULT1A1, but no mutagenicity was observed in the parental cell line. DNA adduct formation in vitro was examined in different human cell lines by thin-layer chromatography 32 P-postlabeling. Whereas 3-NBA formed characteristic DNA adducts in lung A549, liver HepG2, colon HCT116, and breast MCF-7 cells, 2-NBA-derived DNA adducts were only observed in A549 and HepG2 cells, indicating differences in the bioactivation of each isomer. The pattern of 2-NBA-derived DNA adducts in both cell lines consisted of a cluster of up to five adducts. In HepG2 cells DNA binding by 2-NBA was up to 14-fold lower than by 3-NBA. DNA adduct formation of 2-NBA was also investigated in vivo in Wistar rats treated with a single dose of 2, 10, or 100 mg/kg body weight (bw). No DNA adduct formation was detected at doses of up to 10 mg/kg bw 2-NBA, even though 3-NBA induced DNA adducts at a dose of 2 mg/kg bw. Only after administration of one high dose of 100 mg/kg bw 2-NBA was a low level of DNA adduct formation detected, and then only in lung tissue. Density functional theory calculations for both NBAs revealed that the nitrenium ion of the 3-isomer is considerably more stable (~10 kcal/mol) than that of the 2-isomer, providing a possible explanation for the large differences in DNA adduct formation and mutagenicity between 2-and 3-NBA.
Carcinogenesis, 2005
Nitrobenzanthrone (3-NBA) has been isolated from diesel exhaust and airborne particles and identified as a potent direct-acting mutagen in vitro and genotoxic agent in vivo. In order to evaluate the in vivo toxicity and carcinogenicity of 3-NBA in a situation corresponding to inhalation, a combined short-term and lifetime study with intratracheal (i.t.) instillation in female F344 rats was performed. DNA adduct formation, as a marker for the primary effect and analyzed by 32 P-HPLC after single instillation, showed a few major DNA adducts and a rapid increase with a peak after 2 days, followed by a decline. No DNA adducts above the background level were observed after 16 days. The highest DNA adduct formation was observed in lung [$250 DNA adducts/10 8 normal nucleotides (NN)] closely followed by kidney ($200 DNA adducts/10 8 NN), whereas liver contained only 12% ($30 DNA adducts/10 8 NN) of the levels of DNA adducts found in lung. In the tumor study, squamous cell carcinomas were found after 7-9 months in the high-dose group (total dose of 2.5 mg 3-NBA) and after 10-12 months in the low-dose group (total dose of 1.5 mg 3-NBA). The fraction of squamous cell carcinoma out of the total amount of tumors observed at the end of experiment at 18 months, corresponded to 3/16 and 11/16 in the low-and high-dose group, respectively. A single case of adenocarcinoma was also observed in each group. In the control group, no tumors were observed during the entire study of 18 months. In addition, a few cases of squamous metaplasia were also observed in the lung in both dose groups but not in the controls. In conclusion, 3-NBA forms DNA adducts in the lung immediately after i.t. administration but almost all DNA adducts were eliminated after 16 days. Tumor formation in two dose groups was observed in a dose-dependent manner with squamous cell carcinomas as the predominant tumor type at high exposure.
Experimental Cell Research, 2016
3-Nitrobenzanthrone (3-NBA), a potential human carcinogen, is present in diesel exhaust. The main metabolite of 3-NBA, 3-aminobenzanthrone, was detected in urine of miners occupationally exposed to diesel emissions. Environmental and occupational factors play an important role in development of bladder cancer (BC), one of the most frequent malignancies. It is expected that exposure of urothelium to 3-NBA and its metabolites may induce BC initiation and/or progression. To test this hypothesis, we studied geno-and cytotoxicity of 3-NBA using an in vitro BC model. 3-NBA induced higher levels of DNA adducts, reactive oxygen species and DNA breaks in aggressive T24 cells than in more differentiated RT4 cells. To understand the nature of this difference we examined the role of several enzymes that were identified as 3-NBA bio activators. However, the difference in DNA adduct formation cannot be directly linked to the different activity of any of the examined enzymes. Conversely, the difference of tested cell lines in p53 status can partly explain the distinct levels of 3-NBA-DNA adducts and DNA damage induced by 3-NBA. Therefore, we assume that more aggressive T24 cells are more predisposed for DNA adduct formation, DNA damage and, possibly, mutations and as a result further tumorigenesis.
Interdisciplinary Toxicology, 2009
An aromatic amine, o-anisidine (2-methoxyaniline) and its oxidative counterpart, 2-nitroanisole (2-methoxynitrobenzene), are the industrial and environmental pollutants causing tumors of the urinary bladder in rats and mice. Both carcinogens are activated to the same proximate carcinogenic metabolite, N-(2-methoxyphenyl)hydroxylamine, which spontaneously decomposes to nitrenium and/ or carbenium ions responsible for formation of deoxyguanosine adducts in DNA in vitro and in vivo. In other words, generation of N-(2methoxyphenyl)hydroxylamine is responsible for the genotoxic mechanisms of the o-anisidine and 2-nitroanisole carcinogenicity. Analogous enzymes of human and rat livers are capable of activating these carcinogens. Namely, human and rat cytochorme P450 2E1 is the major enzyme oxidizing o-anisidine to N-(2-methoxyphenyl)hydroxylamine, while xanthine oxidase of both species reduces 2-nitroanisole to this metabolite. Likewise, O-demethylation of 2-nitroanisole, which is the detoxication pathway of its metabolism, is also catalyzed by the same human and rat enzyme, cytochorme P450 2E1. The results demonstrate that the rat is a suitable animal model mimicking the fate of both carcinogens in humans and suggest that both compounds are potential carcinogens also for humans.
Oxidative DNA Damage Induced by Carcinogenic Dinitropyrenes in the Presence of P450 Reductase
Chemical Research in Toxicology, 2004
Nitropyrenes are widespread in the environment due to mainly diesel engine emissions. Dinitropyrenes (DNPs), especially 1,8-dinitropyrene (1,8-DNP) and 1,6-dinitropyrene (1,6-DNP), are much more potent mutagens than other nitropyrenes. The carcinogenicity of 1,8-DNP and 1,6-DNP is stronger than 1,3-dinitropyrene (1,3-DNP). It is considered that adduct formation after metabolic activation plays an important role in the expression of carcinogenicity of nitropyrenes. However, Djuric et al. [(1993) Cancer Lett.] reported that oxidative DNA damage was also found as well as adduct formation in rats treated with 1,6-DNP. We investigated oxidative DNA damage by DNPs in the presence of NAD(P)H-cytochrome P450 reductase using 32 P-5′-end-labeled DNA. After P450 reductase treatment, DNPs induced Cu(II)-mediated DNA damage in the presence of NAD(P)H. The intensity of DNA damage by 1,8-DNP or 1,6-DNP was stronger than 1,3-DNP. We also examined synthetic 1-nitro-8-nitrosopyrene (1,8-NNOP) and 1-nitro-6-nitrosopyrene (1,6-NNOP) as one of the metabolites of 1,8-DNP and 1,6-DNP, respectively, to find that 1,8-NNOP and 1,6-NNOP induced Cu(II)-mediated DNA damage in the presence of NAD(P)H but untreated DNPs did not. In both cases of P450 reductase-treated DNPs and NNOPs, catalase and a Cu(I) specific chelator attenuated DNA damage, indicating the involvement of H 2 O 2 and Cu(I). Using a Clarke oxygen electrode, oxygen consumption by the reaction of NNOPs with NAD(P)H and Cu(II) was measured to find that NNOP was nonenzymatically reduced by NAD(P)H and that the addition of Cu(II) promoted the redox cycle. Therefore, these results suggest that DNPs are enzymatically reduced to NNOPs via nitro radical anion and that NNOPs are further reduced nonenzymatically by NAD(P)H. Subsequently, autoxidation of nitro radical anion and the reduced form of NNOP occurs, resulting in O 2generation and DNA damage. We conclude that oxidative DNA damage in addition to DNA adduct formation may play important roles in the carcinogenesis of DNPs via their metabolites.