Tumor multiplicity, DNA adducts and K-ras mutation pattern of 5-methylchrysene in strain A/J mouse lung

A look beyond the priority: A systematic review of the genotoxic, mutagenic, and carcinogenic endpoints of non-priority PAHs

Knowledge of the toxic potential of polycyclic aromatic hydrocarbons (PAHs) has increased over time. Much of this knowledge is about the 16 United States - Environmental Protection Agency (US - EPA) priority PAHs; however, there are other US - EPA non-priority PAHs in the environment, whose toxic potential is underestimated. We conducted a systematic review of in vitro, in vivo, and in silico studies to assess the genotoxicity, mutagenicity, and carcinogenicity of 13 US - EPA non-priority parental PAHs present in the environment. Electronic databases, such as Science Direct, PubMed, Scopus, Google Scholar, and Web of Science, were used to search for research with selected terms without time restrictions. After analysis, following the Preferred Reporting Items for Systematic Reviews and Meta-Analyses (PRISMA) protocol, 249 articles, published between 1946 and 2020, were selected and the quality assessment of these studies was performed. The results showed that 5-methylchrysene (5-MC), 7,12-dimethylbenz[a]anthracene (7,12-DMBA), cyclopenta[cd]pyrene (CPP), and dibenzo[al]pyrene (Db[al]P) were the most studied PAHs. Moreover, 5-MC, 7,12-DMBA, benz[j]aceanthrylene (B[j]A), CPP, anthanthrene (ANT), dibenzo[ae]pyrene (Db[ae]P), and Db[al]P have been reported to cause mutagenic effects and have been being associated with a risk of carcinogenicity. Retene (RET) and benzo[c]fluorene (B[c]F), the least studied compounds, showed evidence of a strong influence on the mutagenicity and carcinogenicity endpoints. Overall, this systematic review provided evidence of the genotoxic, mutagenic, and carcinogenic endpoints of US - EPA non-priority PAHs. However, further studies are needed to improve the future protocols of environmental analysis and risk assessment in severely exposed populations.

Benzo[a]pyrene diol-epoxide (B[a]PDE) upregulates COX-2 expression through MAPKs/AP-1 and IKKbeta/NF-kappaB in mouse epidermal Cl41 cells

Benzo[alpha]pyrene-7,8-diol-9,10-epoxide (B[a]PDE), the major metabolite of benzo[a]pyrene (B[a]P), shows an ultimate complete carcinogen in various animals and is a causative agent for human cancers. However, its effects on the activation of signal pathways and the expression of genes involved in its carcinogenic effect remain largely unknown. In this study, the effects of B[a]PDE on induction of cyclooxygenase (COX)-2 and the signal pathways leading to the induction were investigated. Treatment of mouse epidermal Cl41 cells with B[a]PDE caused an increase in the expression of COX-2 at both transcription and protein levels, while its parental compound B[a]P did not show significant inductive effect. The COX-2 induction by B[a]PDE was dependent on the activation of mitogen-activated protein kinases (MAPK)s/activation protein (AP)-1 pathway, because inhibition of AP-1 by either overexpression of TAM67 (dominant negative mutant of c-jun), or pretreatment of cells with PD98059 (MEK1/2-ERKs pathway inhibitor) or SB202190 (p38K inhibitor), markedly inhibited B[a]PDE-induced COX-2 expression. In addition, impairment of NF-kappaB pathway by either NEMO-BDBP (an NF-kappaB specific inhibitor) or IkappaB kinase (IKK)beta-KM (dominant negative mutant of IKKbeta) also caused marked reduction of COX-2 induction by B[a]PDE. In contrast, inhibition of nuclear factor of activated T cells (NFAT) with FK506, did not show any effect on B[a]PDE-induced COX-2 expression. Collectively, these data indicate that exposure of Cl41 cells to B[a]PDE can induce COX-2 expression by increasing its transcription, which requires the activation of MAPKs/AP-1 and IKKbeta/NF-kappaB pathways, but not NFAT pathway. In view of the importance of COX-2 in carcinogenesis, we anticipate that the induction of COX-2 by B[a]PDE may coordinate its mutagenic effects to facilitate the development of skin cancer.

Effects of polycyclic aromatic hydrocarbons (PAHs) on vascular endothelial growth factor induction through phosphatidylinositol 3-kinase/AP-1-dependent, HIF-1alpha-independent pathway

Previous studies have demonstrated that exposure to polycyclic aromatic hydrocarbons (PAHs) and its derivatives is associated with an increased risk of skin cancers, and the carcinogenic effect of PAHs is thought to involve both tumor initiation and promotion. Whereas PAH tumor initiation is well characterized, the mechanisms involved in the tumor promotion of PAHs remain elusive. In the present study, we investigated the effects of PAHs on vascular endothelial growth factor (VEGF) expression by comparison of its induction between the active metabolite and its parent compound (B[a]PDE versus B[a]P) or between active compound and its relatively inactive analog (5-MCDE versus CDE). We found that exposure of cells to (+/-)-anti-benzo-[a]pyrene-7,8-diol-9,10-epoxide (B[a]PDE) or (+/-)-anti-5-methylchrysene-1,2-diol-3,4-epoxide (5-MCDE) led to marked induction of VEGF in Cl41 cells, whereas benzo[a]pyrene (B[a]P) or chrysene-1,2-diol-3,4-epoxide (CDE) did not exhibit significant inductive effects. Exposure of cells to B[a]PDE and 5-MCDE did not induce HIF-1alpha activation, whereas AP-1 was significantly activated. Moreover, overexpression of TAM67 (a dominant-negative mutant c-Jun) dramatically blocked that VEGF induction. Electrophoretic mobility shift assay showed that AP-1 was only able to specifically recognize and bind to its AP-1 potential binding site within -1136 and -1115 of the VEGF promoter region. Site-directed mutation of this AP-1 binding site eliminated the VEGF transcriptional activity induced by B[a]PDE, suggesting that the AP-1 binding site between -1136 and -1115 in the VEGF promoter region is critical for VEGF induction by B[a]PDE. In addition, overexpression of Deltap85 (a dominant-negative mutant PI-3K) impaired B[a]PDE- and 5-MCDE-induced VEGF induction. Considering our previous findings that PI-3K is an upstream mediator for c-Jun/AP-1 activation, we conclude that the VEGF induction by B[a]PDE and 5-MCDE is through PI-3K/AP-1-dependent and HIF-1alpha-independent pathways. These findings may help us to understand the mechanisms involved in PAH carcinogenic effects.

Genetic alterations in cancer knowledge system: analysis of gene mutations in mouse and human liver and lung tumors

Mutational incidence and spectra for genes examined in both human and mouse lung and liver tumors were analyzed using the National Institute of Environmental Health Sciences (NIEHS) Genetic Alterations in Cancer (GAC) knowledge system. GAC is a publicly available, web-based system for evaluating data obtained from peer-reviewed studies of genetic changes in tumors associated with exposure to chemical, physical, or biological agents, as well as spontaneous tumors. In mice, mutations in Kras2 and Hras-1 were the most common events reported for lung and liver tumors, respectively, whether chemically induced or spontaneous. There was a significant difference in Kras2 mutation incidence for spontaneous versus induced mouse lung tumors and in Hras-1 mutation incidence and spectrum for spontaneous versus induced mouse liver tumors. The major gene changes reported for human lung and liver tumors were in KRAS2 (lung only) and TP53. The KRAS2 mutation incidence was similar for spontaneous and asbestos-induced human lung tumors, while the TP53 mutation incidence differed significantly. Aflatoxin B1, hepatitis B virus, hepatitis C virus, and vinyl chloride all caused TP53 mutations in human liver tumors, but the mutation spectrum for each agent differed. The incidence of KRAS2 mutations in human compared to mouse lung tumors differed significantly, as did the incidence of Hras and p53 gene mutations in human compared to mouse liver tumors. Differences observed in the mutation spectra for agent-induced compared to spontaneous tumors and similarities in spectra for structurally similar agents support the concept that mutation spectra can serve as a "fingerprint" of exposure based on chemical structure.

PI-3K and Akt are mediators of AP-1 induction by 5-MCDE in mouse epidermal Cl41 cells

5-Methylchrysene has been found to be a complete carcinogen in laboratory animals. However, the tumor promotion effects of (+/-)-anti-5-methylchrysene-1,2-diol-3,4-epoxide (5-MCDE) remain unclear. In the present work, we found that 5-MCDE induced marked activator protein-1 (AP-1) activation in Cl41 cells. 5-MCDE also induced a marked activation of phosphatidylinositol 3-kinase (PI-3K). Inhibition of PI-3K impaired 5-MCDE-induced AP-1 transactivation, suggesting that PI-3K is an upstream kinase involved in AP-1 activation by 5-MCDE. Furthermore, we found that Akt is a PI-3K downstream mediator for 5-MCDE-induced AP-1 transactivation, whereas another PI-3K downstream kinase, p70(S6K), was not involved in AP-1 activation by 5-MCDE. Moreover, inhibition of Akt activation blocked 5-MCDE-induced activation of extracellular signal-regulated protein kinases (ERKs) and c-Jun NH(2)-terminal kinases (JNKs), whereas it did not affect p38K activation. Consistently, overexpression of a dominant-negative mutant of ERK2 or JNK1 blocked the AP-1 activation by 5-MCDE. These results demonstrate that 5-MCDE is able to induce AP-1 activation, and the AP-1 induction is specifically through a PI-3K/Akt-dependent and p70(S6K)-independent pathway.

Differential effects of polycyclic aromatic hydrocarbons on transactivation of AP-1 and NF-?B 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.

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.

Polycyclic aromatic hydrocarbons: correlations between DNA adducts and ras oncogene mutations

This review describes a series of studies on the tumorigenic activities of polycyclic aromatic hydrocarbons (PAHs) in various experimental animal model systems, their abilities to form PAH-DNA adducts in target tissues, and their abilities to mutate ras oncogenes in PAH-induced tumors. The review is limited to those PAHs that do not contain nitrogen, for which ras mutations have been detected in induced tumors, and for which some information is available about the structures of the DNA adducts induced in the target tissue. In general, PAHs that form DNA adducts at deoxyadenosine induce mutations at codon 61, whereas those PAHs that form DNA adducts at deoxyguanosine primarily induce mutations at codons 12 or 13. Those PAHs that induce adducts at both bases induce both types of mutations. These correlations provide evidence for the involvement of adduct-directed mutations in ras in the etiology of these tumors. The induced mutation spectra in ras may in fact point back to the identity of the type of adduct formed.

Benzo[a]pyrene diol-epoxide DNA adducts and levels of polycyclic aromatic hydrocarbons in autoptic samples from human lungs

Benzo[a]pyrene (BaP) and other polycyclic aromatic hydrocarbons (PAHs) which are present in cigarette smoke, are common air and food genotoxic contaminants and possible human carcinogens. We measured the following PAH levels: benzo[a]anthracene, benzo[b]fluoranthene, benzo[k]fluoranthene, BaP, dibenzo[a,h]anthracene, benzo[g,h,i]perylene as well as (+/-) syn and anti BaP diol-epoxide (BPDE) DNA adducts in autopsy samples from the lungs of non-smokers, ex-smokers and smokers who had lived in Florence, Italy. PAH levels in lung tissue were similar in all groups, with the exception of dibenzo[a,h]anthracene (DBA), which was higher in lung samples from smokers (n = 10, 0.18+/-0.17 ng/g d.w, mean +/- S.D.) compared to non-smokers (n = 15, 0.046+/-0.025 ng/g d.w) (P < 0.05), whereas ex-smokers (n = 5), had intermediate levels (0.07+/-0.03 ng/g d.w). The average level of total BPDE-DNA adducts was 4.46+/-5.76 per 10(8) bases in smokers, 4.04+/-2.37 per 10(8) in ex-smokers and 1.76+/-1.69 per 10(8) in non-smokers. The levels of non-smokers were significantly different (P < 0.05) from the levels of the smokers and ex-smokers combined. Total BPDE-DNA adducts were correlated with BaP levels in the lung samples in which both determinations were obtained (r = 0.63). Our results demonstrate that the biological load of PAHs due to environmental pollution is similar in individuals who smoke and those who do not, but BPDE-DNA adducts are higher in smokers and ex-smokers compared to non-smokers. This study further confirms the usefulness of BPDE-DNA adduct levels determination in the lungs from autopsy samples for monitoring long-term human exposure to BaP, a representative PAH.

Mechanistic relationships between DNA adducts, oncogene mutations, and lung tumorigenesis in strain A mice

This paper describes a series of studies on the lung tumorigenic activities of polycyclic aromatic hydrocarbons (PAHs) in strain A/J mice, their ability to form PAH-DNA adducts in lung tissues, and their ability to mutate the Ki-ras oncogene in PAH-induced tumors. Seven PAHs were studied: cyclopenta[cd]pyrene (CPP), benzo[a]pyrene (B[a]P), benzo[b]fluoranthene (B[b]F), dibenz[a,h] anthracene (DBA), 5-methylchrysene (5MC), benz[j]aceanthrylene (B[j]A), and dibenzo[a,l]pyrene (DB[a,l]P). The dose-response data for the PAHs revealed 100-fold differences in tumor potency based on dose, with the order of activity DB[a,l]P, DBA > B[j]A > 5MC > CPP B[a]P > B[b]F. Large differences in tumor multiplicity were also observed between the PAHs. DNA adducts were measured by 32P-postlabeling techniques on DNA from lungs of mice treated with these PAH's. DB[a,l]P gave syn- and anti-fjord-region diol-epoxide adducts of dAdo and dGuo; DBA gave both bay-region diol-epoxide-dGuo and bisdihydrodiol-epoxide adducts; CPP gave cyclopenta-ring-dGuo adducts; B[j]A gave a mixture of cyclopenta-ring-dGuo and -dAdo adducts; 5MC gave anti-bay-region diol-epoxide-dGuo adducts; B[a]P gave bay-region diol-epoxide-dGuo adducts; and B[b]F gave 5-hydroxy-B[b]F-diol-epoxide-dGuo adducts. Ki-ras codon 12 and 61 mutation analysis of PAH induced tumors was performed using PCR and dideoxy sequencing methods. DB[a,l]P gave both codon 12 and codon 61 mutations. High proportions of codon 12 TGT mutations from B[a]P-, B[b]F- and 5MC-, induced tumors and CGT mutations from CPP- and B[j]A-induced tumors were observed. DBA produced no mutations in Ki-ras codons 12 or 61 by direct sequencing. The interrelationships between the tumorigenesis, DNA adduct, and oncogene mutation data are discussed.

Introduction to mouse lung tumorigenesis

This article provides a brief overview of some of the characteristics of lung tumors in mice and their application for studies in both chemical and molecular carcinogenesis and in cancer chemoprevention. The reader is referred to the above-mentioned review articles, and the articles to follow in this issue, for more extensive discussions of mouse lung tumorigenesis. It has been very exciting and rewarding to observe the progress made by many dedicated scientists in the field of mouse lung tumorigenesis during the past several years, and I hope that the next few years will be even more exciting.

Mechanistic linkage between DNA adducts, mutations in oncogenes and tumorigenesis of carcinogenic environmental polycyclic aromatic hydrocarbons in strain A/J mice

Five polycyclic aromatic hydrocarbons (PAHs), benzo[a]pyrene (B[a]P), benzo[b]fluoranthene (B[b]F), dibenz[a,h]anthracene (DBA), 5-methylchyrsene (5MC), and cyclopenta[cd]pyrene (CPP) were examined for their lung tumorigenic activities in strain A/J mice, their ability to form PAH-DNA adducts in lung tissues, and their ability to mutate the Ki-ras oncogene in PAH-induced tumors. PAHs dissolved in tricapyrlin were administered by single intraperitoneal injection to male strain A/J mice (20 mice/dose) at doses up to 200 mg/kg depending on the PAH. Animals were sacrificed 8 months later and the lungs removed, fixed, and surface adenomas enumerated. DBA produced maximal tumor multiplicity at the highest dose, 10 mg/kg, giving 32.2 lung adenomas per mouse. At 100 mg/kg, B[a]P, B[b]F, 5MC, and CPP gave 12.8, 5.3, 93.1, and 32.2 lung adenomas per mouse, respectively. The dose response data for each PAH was fit to y = 0.6 + bx1.6, where y is the observed mean lung adenomas per mouse at dose x (in mg/kg), 0.6 is the observed background of lung adenomas per mouse, and b is the fitted constant representing the potency of each PAH. Statistical analysis indicated that the fit of the data to the equation was extremely high with adjusted R2 values > 0.985 and small fit standard errors. Based on this equation, the relative potencies of B[b]F, DBA, 5MC, and CPP compared to B[a]P were PAH (relative activity): DBA (118); 5MC (8.8); CPP (2.9); B[a]P (1.0); B[b]F (0.43). DNA adducts were measured by 32P-postlabeling techniques on DNA from lungs of mice treated with these PAHs. Adducts identified by cochromatography with standards were: from B[a]P, 7R,8S,9S-trihydroxy-10R-(N2-2'-deoxyguanosyl)-7,8,9,10-tetrahydro- B[a]P, and two adducts resulting from the metabolic activation of 9-hydroxy-B[a]P and trans-7,8-dihydroxy-7,8-dihydro-B[a]P; from B[b]F, 5-hydroxy-B[b]F-9,10-diol-11,12-oxide-2'-deoxyguanosine; from DBA, three adducts from the metabolic activation of trans,trans-3,4,10,11-tetrahydroxy-3,4,10,11-tetrahydro-DBA and two anti-DBA-3,4-diol-1,2-oxide-N2-[2'-deoxyguanosine] adducts; from 5MC, 1R,2S,3S-trihydroxy-4-(N2-2'-deoxyguanosyl)-1,2,3,4-tetrahydro- 5MC; from CPP, four CPP-3,4-oxide-2'-deoxyguanosine adducts. Ki-ras codon 12 mutation analysis of PAH-induced tumors was performed using PCR and dideoxy sequencing methods. Mutations from lung tumors from tricaprylin-treated mice were GGT-->GAT, GGT-->CGT, and GGT-->GTT. DBA produced no mutations in Ki-ras codon 12 above spontaneous levels. High proportions (> or = 50%) of GGT-->TGT mutations from B[a]P, B[b]F and 5MC induced tumors and GGT-->CGT mutations from CPP tumors were observed and were statistically significant compared to mutations in tricaprylin control tumors. We conclude from the DNA adduct and Ki-ras mutation studies that bay region diol-epoxide-2'-deoxyguanosine PAH-DNA adducts are associated with the GGT-->TGT mutations, and cyclopenta-ring oxide-2'-deoxyguanosine adducts associated with the GGT-->CGT mutations.