Genotoxic effects of cyclopenta-fused polycyclic aromatic hydrocarbons in different types of isolated rat lung cells

The genotoxic effects of the environmental contaminants benz[j]aceanthrylene (B[j]A), benz[l]aceanthrylene (B[l]A) and benzo[a]pyrene (B[a]P), and the metabolism of radiolabelled B[j]A, were studied using rat lung microsomes and various types of isolated rat lung cells from control and Aroclor 1254 (PCB) treated animals. All three compounds (10 or 20 microg/plate) resulted in low, but detectable, levels of His+ revertants in the Salmonella assay when plated with control lung microsomes. The two cyclopenta polycyclic aromatic hydrocarbons (CP-PAH) B[j]A and B[l]A, gave increased levels of revertants when plated with microsomes from PCB-treated animals. Clara cells, type 2 cells and alveolar macrophages isolated from control rats were exposed to B[j]A, B[l]A or B[a]P (30 microg/ml, 1 h), but neither of the cell types showed any DNA damage when measured by alkaline filter elution. However, both B[j]A and B[l]A (30 microg/ml, 2 h) caused DNA adducts in all three cell types, measured by the 32P-post- labelling technique, whereas no B[a]P adducts were detected (30 microg/ml, 2 h). The total DNA adduct levels in Clara cells, type 2 cells and macrophages exposed to B[j]A were 0.085 +/- 0.033, 0.053 +/- 0.001 and 0.170 +/- 0.030 fmol/microg DNA, respectively, whereas the total levels in cells exposed to B[l]A were 0.140 +/- 0.070, 0.140 +/- 0.030 and 0.220 +/- 0.080 fmol/microg DNA, respectively. Cells exposed to B[j]A revealed only one adduct which corresponds with the B[j]A-1,2- oxide DNA adduct. Judged from high performance liquid chromatography (HPLC) analysis using radiolabelled B[j]A (30 microg/ml, 30 min), the major metabolite formed in control microsomes was B[j]A-1,2-diol. Thus, oxidation at the cyclopenta ring appears to be the most important activation pathway for B[j]A with control rat lung cells. Exposure of lung cells to CP-PAH (30 microg/ml, 2 h) isolated from PCB pretreated rats resulted in slightly increased DNA adduct levels in Clara cells and macrophages when compared to cells isolated from control rats. Furthermore, the adduct pattern had shifted, and no apparent B[j]A-1,2- oxide adduct could be detected on the thin layer chromatography (TLC) plate. In contrast, the major metabolite formed with microsomes from PCB-treated animals was still the B[j]A-1,2-diol.      

Biotransformation of the cyclopenta-fused polycyclic aromatic hydrocarbon benz[j]aceanthrylene in isolated rat liver cells: identification of nine new metabolites

The biotransformation of benz[j]aceanthrylene (B[j]A) was studiedin suspensions of hepatocytes isolated from Aroclor 1254-treatedor untreated rats. Using radiolabeled cofactors and metabolicinhibitors combined with UV, mass and ¹H-NMR spectroscopy, wehave detected five known metabolites and characterized ninenew metabolites: metabolite 1 was tentatively assigned as B[j]A-l,2-dihydrodiol-8-sulfate; metabolite 2, B[j]A-1,2,9,10-tetrahydrotetrol;metabolite 3, B[j]A-1,2-dihydrodiol-10-O-glucuronide; metabolite4, B[j]A-l-one-8-sulfate; metabolite 5, B[j]A-1,2-dihydrodiol-10-sulfate;metabolite 6, the sulfate conjugate of B[j]A-dihydrodiol-phenol;peak 7 in the chromatogram is a mixture of one glutathione conjugateand two sulfate conjugates of a B[j]A-metabolite; metabolite8, B[j]A-10-O-glucuronide; metabolite 8', B[j]A-1,2-dihydrodiol;meta-bolite 9, B[j]A-10-sulfate; metabolite 9', B[j]A-9,10-dihydrodioland metabolite 10, B[j]A-9,10-dihydro-9-hydroxy-10-sulfate.The metabolites identified support the notion that epoxidationat the cyclopenta region is an important activation step ofB[j]A. Furthermore, sulfation appears to play a very importantrole in the conversion of hydroxylated B[j]A metabolites intomore polar excretable products.     

Resistant hepatocytes as early changes in liver induced by polycyclic aromatic hydrocarbons

Induction of putative preneoplastic hepatocytes which are resistant to cytotoxic effect of 2-acetylaminofluorene (2-AAF) by five carcinogenic polycyclic aromatic hydrocarbons (PAH) was tested using gamma-glutamyl transpeptidase (gamma-GT) as a histochemical marker enzyme. Benzo (a) pyrene [B(a)P], 7,12-dimethylbenz(a) anthracene (7,12-DMBA), 3-methylcholanthrene (3-MC), dibenz (a,h)-anthracene [DB(a, h)A] and benzo (a) anthracene [B(a)A] were given 12 h after partial hepatectomy (PH) followed by 2-AAF and carbon tetrachloride (CCI4) feeding, a procedure developed by this laboratory. All of the five PAHs induced a signficantly increased number of gamma-GT positive foci when compared with sham-hepatectomized (SH) or vehicle control groups. The numbers of gamma-GT-positive foci induced by B(as)P, 7,12-DMBA, 3-MC and DB (a,h)A were significantly different from all of the parent compounds, anthracene, naphthalene, pyrene and phenanthrene. B(a)A did not induce significantly increased number of foci only when compared to anthracene. Possible usefulness of this system for in vivo short-term assay is discussed.     

Smoking increases carcinogenic polycyclic aromatic hydrocarbons in human lung tissue

Tobacco smoke is a major source of human exposure to polycyclic aromatic hydrocarbons (PAHs). The concentration of PAHs in lung tissue would reflect an individual's dose, and its variation could perhaps reflect cancer risk. Eleven PAHs were measured in 70 lung tissue samples from cancer-free autopsy donors by gas chromatography-mass spectrometry. There were 37 smokers and 33 nonsmokers as estimated by serum cotinine concentration. The sum of PAH concentrations was higher in smokers (P = 0.01), and there was a dose-response relationship for greater smoking (P < 0.01). Smoking increased the concentration of five PAHs including benzo(a)pyrene, which increased approximately 2-fold. The risk for increasing carcinogenic PAHs (odds ratio, 8.20; 95% confidence interval, 2.39-28.09) was 3-fold compared with noncarcinogenic PAHs (odds ratio, 2.61; 95% confidence interval, 0.75-9.12). A higher concentration of PAHs was detected in the lung tissue of males, although the estimated smoking was similar in males and females. Race was not associated with PAH concentrations overall, but PAH concentrations appeared to be higher in African-American males than in any other group. Age was weakly correlated with an increase in fluoranthene and pyrene. The measurement of PAHs in human lung tissue can be used to estimate the actual dose to the target organ.     

Targeting of lung cancer mutational hotspots by polycyclic aromatic hydrocarbons

BACKGROUND: Polycyclic aromatic hydrocarbons (PAHs) are ubiquitous in combustion products of organic matter, including cigarette smoke. Metabolically activated diol epoxides of these compounds, including benzo[a]pyrene diol epoxide (B[a]PDE), have been suggested as causative agents in the development of lung cancer. We previously mapped the distribution of B[a]PDE adducts within the p53 tumor suppressor gene (also known as TP53), which is mutated in 60% of human lung cancers, and found that B[a]PDE adducts preferentially form at lung cancer mutational hotspots (codons 154, 157, 158, 245, 248, and 273). Other PAHs may be important in lung cancer as well. METHODS: Here we have mapped the distribution of adducts induced by diol epoxides of additional PAHs: chrysene (CDE), 5-methylchrysene (5-MCDE), 6-methylchrysene (6-MCDE), benzo[c]phenanthrene (B[c]PDE), and benzo[g]chrysene (B[g]CDE) within exons 5, 7, and 8 of the p53 gene in human bronchial epithelial cells. RESULTS: CDE exposure produced only low levels of adducts. Exposure of cells to the other activated PAHs resulted in DNA damage patterns similar to those previously observed with B[a]PDE but with some distinct differences. 5-MCDE, 6-MCDE, B[g]CDE, and B[c]PDE efficiently induced adducts at guanines within codons 154, 156, 157, 158, and 159 of exon 5, codons 237, 245 and 248 of exon 7, and codon 273 of exon 8, but the relative levels of adducts at each site varied for each compound. B[g]CDE, B[c]PDE, and 5-MCDE induced damage at codon 158 more selectively than 6-MCDE or B[a]PDE. The sites most strongly involved in PAH adduct formation were also the sites of highest mutation frequency (codons 157, 158, 245, 248, and 273). CONCLUSION: The data suggest that PAHs contribute to the mutational spectrum in human lung cancer.     

Cytotoxic and transformation responses of rat tracheal epithelial cells exposed to nitrated polycyclic aromatic hydrocarbons in culture

Four nitropolycyclic aromatic hydrocarbons (NPAHs) were investigated for their cytotoxic effects on rat tracheal epithelial (RTE) cells. 6-Nitrochrysene (6-NC), 1,6-dinitropyrene (1,6-DNP), 1-nitropyrene (1-NP) and 4-nitropyrene (4-NP) induced dose-dependent decreases in the relative colony-forming efficiency (RCFE) of RTE cells. The compounds could be separated into two groups based on their cytotoxic potencies, a group that displayed high cytotoxic effects (6-NC and 1,6-DNP), and a group that displayed low cytotoxic effects (1-NP and 4-NP). The most cytotoxic compound was 6-NC, with an ED50 of 0.13 microM, followed by 1,6-DNP, 4-NP and 1-NP with ED50s of 1.25, 8.9 and 9.1 microM, respectively. The most cytotoxic compound (6-NC) and one of the components with low cytotoxicity (1-NP) were assayed for their ability to induce preneoplastic transformation of RTE cells using equally toxic doses of both compounds. The frequencies of transformation induced by 6-NC in cells isolated from control animals or from animals pretreated with 3-methylcholanthrene (3-MC) were 8.4 X 10(-3) and 21.4 X 10(-3), respectively. 1-NP did not induce cell transformation. Equally toxic doses of the direct acting carcinogen N-methyl-N'-nitro-N-nitrosoguanidine, used as a positive control, induced transformation frequencies of 8.7 X 10(-3) and 6.4 X 10(-3) in cells isolated from control animals or from animals pretreated with 3-MC, respectively. These studies show that RTE cells have the metabolic capacity to activate NPAHs to toxic metabolites; thus, the RTE system should be very useful for evaluating the potential toxic effects of this ubiquitous class of airborne pollutants. In addition, the observed differences in cellular toxicity and transformation capabilities of 6-NC and 1-NP were consistent with the results of other studies that demonstrated the greater potency for induction of tumors in animals of 6-NC relative to 1-NP.     

Food restriction increases detoxification of polycyclic aromatic hydrocarbons in the rat.

It is well known that food restriction diminishes tumor formation, but mechanisms responsible are difficult to define because multiple physiological changes result from dietary alterations. Studies in this report were designed to focus specifically on the effects of food restriction on hepatic metabolism of polycyclic aromatic hydrocarbons following liver transplantation. By placing livers from food-restricted and untreated rats into naive controls, the effects of diet could be restricted to the liver. After a 15 min infusion of [3H]benzo[a]pyrene under these conditions, food restriction increased polar metabolites in liver (70 pmol/g) and blood (8 pmol/ml) compared to controls approximately 2-fold. Four hours after liver transplantation, levels of polar metabolites in blood were diminished by approximately 50% but were still approximately 2-fold higher in the food-restricted than in the control group. Lung, kidney, spleen, adrenal, ovary, colon, heart and brain also contained higher levels of polar metabolites in the food-restricted than in the control group. The more hydrophobic glucuronides and sulfate conjugates accounted for most of the elevation in polar metabolites in blood from the food-restricted group. In spite of the increase in circulating metabolites in blood of food-restricted animals, DNA binding in liver, lung and kidney was identical in tissues from control and food-restricted groups. In order to evaluate the hypothesis that food restriction stimulated the release of hepatic benzo[a]pyrene metabolites, a liver perfusion model was employed. Maximal rates of release of polar metabolites into the effluent perfusate were approximately 30 and approximately 45 nmol/g/h in livers of control and food-restricted rats respectively. Moreover, rates of metabolism of the model compound p-nitroanisole and glucuronidation of p-nitrophenol were also approximately 2-fold higher in livers from food-restricted than control rats. However, rates of monooxygenation were the same in microsomes prepared from livers of food-restricted or control animals. These results support the hypothesis that food restriction enhances the supply of cofactors which stimulate metabolism of polycyclic aromatic hydrocarbons. This detoxification process may be an important mechanism involved in the protective action of reduced food intake.     

Comparative tumorigenicity of the cyclopenta-fused polycyclic aromatic hydrocarbons aceanthrylene, dihydroaceanthrylene and acephenanthrylene in preweanling CD-1 and BLU:Ha mouse bioassays.

Cyclopenta-fused polycyclic aromatic hydrocarbons are ubiquitous environmental pollutants and potential human health biohazards. In this study, the tumorigenicity of three single cyclopenta-fused polycyclic aromatic hydrocarbons, aceanthrylene, dihydroaceanthrylene and acephenanthrylene, was examined in preweanling CD-1 and BLU:Ha mouse bioassays at total doses of 175, 437.5 and 875 micrograms/mouse. No death or significant toxicity was observed with the treatment protocol in the tested animals. In CD-1 mice, a significant increase in lung tumor incidence (18-26%, P < 0. 025-0.01) for these three compounds was recorded in animals treated with 875 micrograms as compared with the control animals (3%). Significant numbers of liver tumors (25-41%, P < 0.01-0.001) were induced in all aceanthrylene treatment groups and in animals treated with 875 micrograms acephenanthrylene (35%) at the termination at 9 months. Most liver tumors were induced in male animals. The ED50 values were estimated as 8.5, 10.6 and 12.8 micromol and the TM1.0 were 15.1, 20.4 and 23.1 micromol for aceanthrylene, acephenanthrylene and dihydroaceanthrylene, respectively. In BLU:Ha mice, there was a significant dose-dependent increase in lung tumor incidence, from 4% for the control group to 33% (P < 0.001) for the animals treated with 875 micrograms aceanthrylene and to 24% (P < 0.02) for the animals treated with 437.5 micrograms acephenanthrylene. The ED50 values were 6.0 and 4.4 micromol and the TM1.0 were 9.8 and 6.8 micromol for aceanthrylene and acephenanthrylene, respectively. No significant difference in lung tumor incidence between male and female mice was found. Based on these data and comparisons of tumorigenic potency with other polycyclic aromatic hydrocarbons previously tested in these newborn mouse bioassays, aceanthrylene and acephenanthrylene were classified as weak tumorigens.     

Human breast cell-mediated mutagenesis of mammalian cells by polycyclic aromatic hydrocarbons

A system has been developed in which human breast cells activate chemical procarcinogens to mutagenic compounds. The degree of activation is quantitated by the estimation of induction of 6-thioguanine-resistant specific locus mutants in a cocultured Chinese hamster V-79 cell population which does not activate carcinogens. Both mammary stromal and parenchymal cells could activate the procarcinogen 7,12-dimethylbenz(a)anthracene. In addition, it is shown that the two mammary cell populations converted both 7,12-dimethylbenz(a)anthracene and benzo(a)pyrene to water-soluble metabolites. The stromal cells produced substantial amounts of glucuronic acid conjugates, but the parenchymal cells did not. Both cell types metabolize benzo(a)pyrene to the organic-soluble metabolites 9,10- and 7,8-dihydrodiol and both 9- and 3-hydroxybenzo(a)pyrene. These results suggest that the human breast may be a target for polycyclic aromatic hydrocarbon carcinogenesis.     

Differential effects of polycyclic aromatic hydrocarbons on transactivation of AP-1 and NF-kappaB in mouse epidermal cl41 cells

Polycyclic aromatic hydrocarbons (PAHs) and their derivatives, such as benzo[a]pyrene (B[a]P), (+/-)-anti-benzo[a]pyrene-7,8-diol-9,10-epoxide (B[a]PDE), and 5-methylchrysene-1,2-diol-3,4-epoxide (5-MCDE), are complete carcinogens. However, the tumor promotion effects of PAHs remain unclear. We therefore investigated the possible activation of activator protein-1 (AP-1) and nuclear factor-kappaB (NFkappaB) in mouse epidermal Cl41 cells after different PAHs treatments, including B[a]P, B[a]PDE, chrysene-1,2-diol-3,4-epoxid (CDE), and 5-MCDE. The results showed that B[a]PDE and 5-MCDE were able to activate AP-1 and NF-kappaB, whereas B[a]P showed only marginal effect on AP-1 activation, and B[a]P and CDE had no effect on NF-kappaB activation. Treatment with either B[a]PDE or 5-MCDE also resulted in mitogen-activated protein kinases (MAPKs) activation as well as inhibitory subunit kappa-B (IkappaBalpha) phosphorylation and degradation, whereas B[a]P and CDE had no effect. Pretreatment with PD98059, a specific inhibitor for extracellular signal-regulated protein kinases (ERKs) upstream kinase MEK1/2, or SB202190, a p38 kinase inhibitor, resulted in a dramatic inhibition of B[a]PDE-induced AP-1 transactivation. In addition, B[a]PDE-induced AP-1 activation was also inhibited by overexpressing a dominant negative mutant of JNK1 in the cells. All these suggest ERKs, c-jun N-terminal kinases (JNKs), and p38 kinase signal transduction pathways are required for AP-1 induction by B[a]PDE. Taken together, B[a]PDE and 5-MCDE are the active compounds of PAHs to initiate signaling pathways. Considering the important roles of AP-1 and NF-kappaB in tumor promotion, we speculated the activation of AP-1 and NF-kappaB by B[a]PDE and 5-MCDE may involve in their or their parent compounds' tumor promotion effects. This study may help in better understanding the tumor promotion effects of PAHs.     

多环芳烃与乳腺癌的相关性

随着交通工具及现代工业的发展,多环芳烃(PAHs)在空气中的含量逐步增加。乳腺癌作为一种女性常见的恶性肿瘤,发病率逐年上升。部分病因学研究表明,PAHs等环境污染物与乳腺癌存在一定的相关性。PAHs进入机体后,不仅能被代谢解毒,而且也可经代谢而被活化,形成致癌物质。笔者主要从PAHs的体内代谢、关键酶和代谢产物方面进行文献整理,并对当前PAHs与乳腺癌相关性的研究进行总结,进一步探讨PAHs在乳腺癌发病中的作用,以期为乳腺癌的预防和治疗提供新途径。     

Contribution of polycyclic aromatic hydrocarbons and polar polycyclic aromatic compounds to the carcinogenic impact of flue gas condensate from coal-fired residential furnaces evaluated by implantation into the rat lung

For identification of the substances chiefly responsible for the carcinogenic action of the emission condensate from coal-fired residential furnaces, the implantation method was used as a carcinogen-specific bioassay for comparison of the carcinogenic effect of various fractions with that of a total sample of flue gas condensate tested in 2 or 3 different doses. After implantation into the lungs of Osborne-Mendel rats, the condensate from coal-fired residential furnaces, a fraction containing polycyclic aromatic hydrocarbons (PAHs) and thiaarenes [sulfur-containing polycyclic aromatic compounds (S-PACs)] with 4-7 rings, as well as fraction containing more polar polycyclic aromatic compounds (PACs) and PAHs with higher molecular weight, induced lung carcinomas and sarcomas. According to probit analysis, the fraction containing PAHs plus S-PACs with 4-7 rings accounted for about 68.2% of the total carcinogenicity of flue gas condensate, whereas the fraction containing more polar PACs and higher PAHs accounted for about 54.6%. All other fractions, such as nonaromatic compounds and PACs with 2 and 3 rings, constituting about 70% of the weight of the total condensate, seemed not to be carcinogenic. Only 1.4% of the total carcinogenicity of the flue gas condensate was found to be attributable to the amount of benzo[a]pyrene (CAS: 50-32-8) present in the condensate (1.14 mg/g condensate). The contribution of more than 100% of both active fractions to the total carcinogenicity (68.2 and 54.6%) may suggest an interrelation of the fractions.     

Interspecies comparison of human and rat mammary epithelial cell-mediated mutagenesis by polycyclic aromatic hydrocarbons

In order to compare the interactions of procarcinogens with mammary cells from humans and rats, a uniform set of mediated mutagenesis assays has been established. In these assays, species-specific mammary epithelial cells activate procarcinogens, and specific locus mutations are quantitated in cocultured V-79 cells. Mutations were induced in the rat mammary cell coculture system exposed to 7,12-dimethylbenz(a)anthracene but not benzo(a)pyrene. In contrast, in the human mammary cell coculture system benzo(a)pyrene was much more effective than 7,12-dimethylbenz(a)anthracene in the induction of mutations. These results suggest caution in extrapolating carcinogenesis data between rodents and humans. They also suggest that the relationship between the ubiquitous environmental xenobiotic benzo(a)pyrene and the etiology of human breast cancer requires further exploration.     

An overview of immunotoxicology and carcinogenic polycyclic aromatic hydrocarbons

3-Chloro-4-(dichloromethyl)-5-hydroxy-2(5H)-furanone, better known by its historical name ‘mutagen X’ or MX, is a chlorination disinfection byproduct that forms from the reaction of chlorine and humic acids in raw water. MX has been measured in drinking water samples in several countries at levels that ranged from non-detectable to 310 ng/L. Although the concentration of MX in drinking water is typically 100- to 1000-fold lower than other common chlorinated by-products of concern (e.g., trihalomethanes), some have hypothesized that MX might play a role in the increased cancer risks that have been associated with the consumption of chlorinated water. This hypothesis is based on observations that MX, in some test systems, is extremely potent relative to trihalomethanes in inducing DNA damage and altering pathways involved in cell growth, and that in some epidemiological studies increased cancer rates are associated with the bacterial mutagenicity of disinfected water of which MX contributes a significant portion. MX also appears to be more potent than other chlorination by-products in causing cancer in animals. This article reviews the available evidence on the carcinogenicity of MX. MX induced cancer at multiple sites in male and female rats, acted as a tumor initiator and promoter, enhanced tumor yields in genetically modified rodents, induced a myriad of genotoxic effects in numerous in vitro and in vivo test systems, and was a potent inhibitor of gap junction intercellular communication. Although the precise mechanism of MX-induced DNA damage is not known, MX is able to cause DNA damage through an unusual mechanism of ionizing DNA bases due to its extremely high reductive potential. MX may also cause mutations through DNA adduction. This article develops a mean cancer potency estimate for MX of 2.3 (mg/kg-d)^?1 and an upper 95% percentile estimate of 4.5 (mg/kg-d)^?1, and examines the potential health risks posed by this chlorination contaminant in drinking water. A discussion of additional data that would be desirable to better characterize the risks posed by MX and other halogenated hydroxyfuranones follows.     

多环芳烃水平与人类直肠癌发生相关性的研究

目的:探讨多环芳烃(PAHs)在人类直肠癌发生过程中的作用。方法:直肠癌组织、癌旁组织和非直肠癌患者的直肠组织中的PAHs分别经超声提取,固相萃取净化和高效液相色谱荧光分析。结果:3组标本中共检出4种PAHs,分别是菲、芘、2-甲基蒽和苯并(a)芘。其中芘、2-甲基蒽和苯并(a)芘在直肠癌组织和癌旁组织中的含量均高于非直肠癌患者的直肠组织,差异有统计学意义,P<0.05;菲在3组标本中的含量差异无统计学意义,P>0.05;4种PAHs在直肠癌组织与癌旁组织中的含量差异均无统计学意义,P>0.05。结论:人类直肠组织中存在PAHs;人类直肠组织中PAHs的含量与直肠癌的发生有一定的相关性。