Mutagenicity of selected polycyclic aromatic hydrocarbons (PAHs) (original) (raw)
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Mutation Research-genetic Toxicology and Environmental Mutagenesis, 2002
Benzo[a]pyrene (B[a]P) is the most thoroughly studied polycyclic aromatic hydrocarbon (PAH). Many mechanisms have been suggested to explain its carcinogenic activity, yet many questions still remain. K-region dihydrodiols of PAHs are metabolic intermediates depending on the specific cytochrome P450 and had been thought to be detoxification products. However, K-region dihydrodiols of several PAHs have recently been shown to morphologically transform mouse embryo C3H10T1/2CL8 cells (C3H10T1/2 cells). Because K-region dihydrodiols are not metabolically formed from PAHs by C3H10T1/2 cells, these cells provide a useful tool to independently study the mechanisms of action of PAHs and their K-region dihydrodiols. Here, we compare the morphological cell transforming, DNA damaging, and DNA adducting activities of the K-region dihydrodiol of B[a]P, trans-B[a]P-4,5-diol with B[a]P. Both trans-B[a]P-4,5-diol and B[a]P morphologically transformed C3H10T1/2 cells by producing both Types II and III transformed foci. The morphological cell transforming and cytotoxicity dose response curves for trans-B[a]P-4,5-diol and B[a]P were indistinguishable. Since morphological cell transformation is strongly associated with mutation and/or larger scale DNA damage in C3H10T1/2 cells, the identification of DNA damage induced in these cells by trans-B[a]P-4,5-diol was sought. Both trans-B[a]P-4,5-diol and B[a]P exhibited significant DNA damaging activity without significant concurrent cytotoxicity using the comet assay, but with different dose responses and comet tail distributions. DNA adduct patterns from C3H10T1/2 cells were examined after trans-B[a]P-4,5-diol or B[a]P treatment using 32 P-postlabeling techniques and improved TLC elution systems designed to separate polar DNA adducts. While B[a]P treatment produced one major DNA adduct identified as anti-trans-B[a]P-7,8-diol-9,10-epoxide-deoxyguanosine, no stable covalent DNA adducts were detected in the DNA of trans-B[a]P-4,5-diol-treated cells. In summary, this study provides Abbreviations: ara-C, cytosine arabinoside; B[a]P, benzo[a]pyrene; BNF, -naphthoflavone; C3H10T1/2, C3H10T1/2CL8; trans-B[a]P-4,5-diol, (±) trans-4,5-dihydro-4,5-dihydroxyB[a]P; BPDE, anti-trans-B[a]P-7,8-diol-9,10-epoxide; MMS, methyl methanesulfonate; PAH, polycyclic aromatic hydrocarbon; ROS, reactive oxygen species ଝ The research described in this article has been reviewed by the National Health and Environmental Effects Research Laboratory, U.S. Environmental Protection Agency and approved for publication. Approval does not signify that the contents necessarily reflect the views of the Agency nor does mention of trade names or commercial products constitute endorsement or recommendation for use. (S. Nesnow). 1383-5718/02/$ -see front matter. Published by Elsevier Science B.V. PII: S 1 3 8 3 -5 7 1 8 ( 0 2 ) 0 0 2 1 8 -8
Mutation Research/Genetic Toxicology and Environmental Mutagenesis, 2016
Benzo[a]pyrene (B[a]P) is a known genotoxicant and carcinogen, yet its genotoxic response at low level exposure has not been determined. This study was conducted to examine the interplay of dose and metabolic capacity on the genotoxicity of B[a]P. An improved understanding the biological significance of low level chemical exposures will help to improve human health risk assessments. The genotoxic and mutagenic effects of B[a]P were investigated using human cell lines AHH-1, MCL-5, TK6 and HepG2, with differential expression of the CYP450 enzymes (CYP1A1, 1B1 and1A2) involved in B[a]P metabolism. MCL-5 and HepG2 cells showed detectable basal expression and activity of CYP1A1, 1B1 and 1A2 as compared to AHH-1, which only show CYP1A1 basal expression and activity. TK6 cells showed negligible expression levels of all three CYP450 enzymes. In vitro micronucleus and the hypoxanthine phosphoribosyltransferase assays were conducted to determine the effect of B[a]P on chromosome damage and point mutation induction. After 24h exposure, concentration-dependent increases in micronucleus (MN) frequency were observed in all cell lines except TK6. After 4h exposure, only the metabolically competent cell lines MCL-5 and HepG2 showed MN induction (with a threshold concentration at 25.5µM from MCL-5 cells) indicating the importance of exposure time for genotoxicity. The HPRT assay also displayed concentration-dependent increases in mutant frequency in MCL-5 cells, after 4h and 24h treatments. Mutation spectra analysis of MCL-5 and AHH-1 HPRT mutants revealed frequent B[a]P induced G to T transversion mutations (72% and 44% of induced mutations in MCL-5 and AHH-1, respectively). This study therefore demonstrates a key link between metabolic capability, B[a]P exposure time and genotoxicity.
Toxicology Letters, 2010
Exposure to polycyclic aromatic hydrocarbons (PAHs) has been positively associated with prostate cancer, but knowledge of the formation of PAH-DNA adducts and related genotoxic events in prostatic cells is limited. In the present study, benzo[a]pyrene (BaP), a potent mutagenic PAH, formed significant levels of DNA adducts in cell lines derived from human prostate carcinoma. When analyzing the effect of BaP on the induction of CYP1 enzymes participating in the metabolic activation of PAHs in LNCaP cells, we found that BaP induced expression of CYP1A1 and CYP1A2, but not CYP1B1 enzyme. Despite a significant amount of DNA adducts being formed by BaP and, to a lesser extent also by another strong genotoxin, dibenzo[a,l]pyrene, neither apoptosis nor cell-cycle arrest were induced in LNCaP cells. LNCaP cells were not sensitized to the induction of apoptosis by PAHs even through inhibition of the phosphoinositide-3-kinase/Akt pro-survival pathway. The lack of apoptosis was not due a disruption of expression of pro-apoptotic and pro-survival members of the Bcl-2 family of apoptosis regulators. In contrast to other genotoxic stimuli, genotoxic PAHs failed to induce DNA double-strand breaks, as illustrated by the lack of phosphorylation of histone H2AX or checkpoint kinase-2. BaP did not activate p53, as evidenced by the lack of p53 accumulation, phosphorylation at Ser15, or induction of p53 transcriptional targets. Taken together, although genotoxic PAHs produced significant levels of DNA adducts in a model of human prostate carcinoma cells, they did not activate the mechanisms leading to elimination of cells with significant damage to DNA, presumably due to their failure to activate the p53-dependent DNA damage response.
DNA Repair, 2011
Polycyclic aromatic hydrocarbons (PAH) are an important class of environmental contaminants many of which require metabolic activation to DNA-reactive bay or fjord region diolepoxides (DE) in order to exert their mutagenic and carcinogenic effects. In this study, the mutagenicity of the bay region diolepoxides (+)-anti-7,8-dihydroxy-9,10-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene (BPDE) and (±)-anti-1,2-dihydroxy-3,4-epoxy-1,2,3,4-tetrahydrodibenzo[a,h]anthracene (DBADE) and the fjord region diolepoxides (±)-anti-11,12-dihydroxy-13,14-epoxy-11,12,13,14-tetrahydrodibenzo[a,l]-pyrene (DBPDE) and (±)-anti-3,4-dihydroxy-1,2-epoxy-1,2,3,4-tetrahydrobenzo[c]-phenanthrene (BPhDE) was compared in nucleotide excision repair (NER) proficient and deficient hamster cell lines. The 32 Ppostlabelling assay was applied to analyze DNA adduct levels and the Hprt gene mutation assay for monitoring mutations. Previously, we found that the mutagenicity per adduct was four times higher for DBPDE compared to BPDE in NER proficient cells. In these same cells, the mutagenicity of DBADE and BPhDE adducts was now found to be significantly lower compared to that of BPDE. In NER deficient cells the highest mutagenicity per adduct was found for BPDE and there was a tenfold and fivefold difference when comparing the BPDE data with the DBADE and BPhDE data, respectively. In order to investigate to what extent the mutagenicity of the different adducts in NER proficient cells was influenced by repair or replication bypass, we measured the overall NER incision rate, the rate of adduct removal, the rate of replication bypass and the frequency of induced recombination in the Hprt gene. Since NER turned out to be an important pathway for the yield of mutations, we further analyzed the role of transcription coupled NER versus global genome NER. However, our data demonstrate that neither of these pathways seems to be the sole factor determining the mutation frequency of the four PAH-DE and that the differences in the repair efficiency of these compounds could not be related to the presence of a bay or fjord region in the parent PAH.
Genotoxicity of Heterocyclic PAHs in the Micronucleus Assay with the Fish Liver Cell Line RTL-W1
PLoS ONE, 2014
Heterocyclic aromatic hydrocarbons are, together with their un-substituted analogues, widely distributed throughout all environmental compartments. While fate and effects of homocyclic PAHs are well-understood, there are still data gaps concerning the ecotoxicology of heterocyclic PAHs: Only few publications are available investigating these substances using in vitro bioassays. Here, we present a study focusing on the identification and quantification of clastogenic and aneugenic effects in the micronucleus assay with the fish liver cell line RTL-W1 that was originally derived from rainbow trout (Oncorhynchus mykiss). Real concentrations of the test items after incubation without cells were determined to assess chemical losses due to, e.g., sorption or volatilization, by means of gas chromatography-mass spectrometry. We were able to show genotoxic effects for six compounds that have not been reported in vertebrate systems before. Out of the tested substances, 2,3-dimethylbenzofuran, benzothiophene, quinoline and 6-methylquinoline did not cause substantial induction of micronuclei in the cell line. Acridine caused the highest absolute induction. Carbazole, acridine and dibenzothiophene were the most potent substances compared with 4-nitroquinoline oxide, a well characterized genotoxicant with high potency used as standard. Dibenzofuran was positive in our investigation and tested negative before in a mammalian system. Chemical losses during incubation ranged from 29.3% (acridine) to 91.7% (benzofuran) and may be a confounding factor in studies without chemical analyses, leading to an underestimation of the real potency. The relative potency of the investigated substances was high compared with their un-substituted PAH analogues, only the latter being typically monitored as priority or indicator pollutants. Hetero-PAHs are widely distributed in the environment and even more mobile, e.g. in ground water, than homocyclic PAHs due to the higher water solubility. We conclude that this substance class poses a high risk to water quality and should be included in international monitoring programs.
Food and Chemical Toxicology, 1986
The interdisciplinary evaluation of risks from carcinogens utilizes, inter alia, data on the activities of the compounds in short-term assays. A systematic approach is being used to determine (a) mutagenesis in bacteria (the study of direct activities and specific modes of metabolic activation), (b) DNA damage within primary mammalian cells (DNA single-strand breaks and persistence of damage, by a method extendable to the in vivo situation) and (c) amplified DNA sequences in cultured cells (as an endpoint probably relevant to carcinogenesis). This test combination was expected to reduce some of the shortcomings of other batteries of tests, which suffer from a lack of appropriate metabolic conversion of compounds, irrelevancy of genetic endpoints and pharmacokinetic limitations. Furthermore, as each assay in the test strategy differs from the others only by one of the parameters described above, a reasonable understanding of divergent test results from assay to assay was anticipated. Several substances were investigated to elucidate why their activities in short-term assays and in carcinogenesis experiments do not correlate. The substances were N-nitrodimethylamine, for which formaldehyde is the reactive intermediate in bacterial mutagenesis but not in mammalian cells or in vivo, N-nitrosodiethanolamine, a carcinogen that must be activated by external alcohol dehydrogenase to be mutagenic in bacteria, N-nitrosodialkylamines, with unique organotropism in vivo for which organ-specific activation was studied in vitro, N-nitroso compounds that are inactivated in vivo but not in vitro, and components of the aristolocbic acid mixture which may be metabolized oxidatively or reductively, as well as numerous miscellaneous compounds that were expected to be genotoxins on account of their chemical structure. In addition to the assessment of genotoxicity, the results obtained in individual tests of this strategy yield important data on mechanisms of activity, such as organ-specific activation and deactivation, species variations, in vitro~in vivo correlation and persistence or repair of damage.
Genotoxic Effects of Benzo[a]pyrene and Dibenzo[a,l]pyrene in a Human Lung Cell Line
International Journal of Toxicology, 2006
Several studies have shown that polycyclic aromatic hydrocarbons (PAHs) produce genotoxic effects in assays performed in vivo and in vitro. This study was undertaken to investigate the ability of benzo[ a]pyrene (BP) and dibenzo[ a,l]pyrene (DBP) to induce DNA damage in a human lung fibroblast cell line (MRC-5), using sister-chromatid exchanges test (SCEs), the comet assay, and evaluating point mutations in codon 12 of the K- ras protooncogene by polymerase chain reaction–single-strand conformation polymorphisms (PCR-SSCPs) and restriction fragment length polymorphisms (RFLP)-enriched PCR methods. Sister-chromatid exchanges frequencies were significantly increased in cells exposed to benzo[ a]pyrene and dibenzo[ a,l]pyrene in relation to controls ( p < .001). Using the standard alkaline comet assay, significant differences between groups were found for the variable comet moment (CM) when cells were exposed to BP ( p < .001) and DBP ( p < .001). Nevertheless, PCR-SSCP and RF...