Mechanistic Evaluation of Black Cohosh Extract-Induced Genotoxicity in Human Cells.

Black cohosh extract (BCE) is marketed to women as an alternative to hormone replacement therapy for alleviating menopausal symptoms. Previous studies by the National Toxicology Program revealed that BCE induced micronuclei (MN) and a nonregenerative macrocytic anemia in rats and mice, likely caused by disruption of the folate metabolism pathway. Additional work using TK6 cells showed that BCE induced aneugenicity by destabilizing microtubules. In the present study, BCE-induced MN were confirmed in TK6 and HepG2 cells. We then evaluated BCE-induced DNA damage using the comet assay at multiple time points (0.5-24 h). Following a 0.5-h exposure, BCE induced significant, concentration-dependent increases in %tail DNA in TK6 cells only. Although DNA damage decreased in TK6 cells over time, likely due to repair, small but statistically significant levels of DNA damage were observed after 2 and 4 h exposures to 250 µg/ml BCE. A G1/S arrest in TK6 cells exposed to 125 µg/ml BCE (24 h) was accompanied by apoptosis and increased expression of γH2A.X, p-Chk1, p-Chk2, p53, and p21. Conditioning TK6 cells to physiological levels of folic acid (120 nM) did not increase the sensitivity of cells to BCE-induced DNA damage. BCE did not alter global DNA methylation in TK6 and HepG2 cells cultured in standard medium. Our results suggest that BCE induces acute DNA strand breaks which are quickly repaired in TK6 cells, whereas DNA damage seen at 4 and 24 h may reflect apoptosis. The present study supports that BCE is genotoxic mainly by inducing MN with an aneugenic mode of action.

Dose and temporal evaluation of ethylene oxide-induced mutagenicity in the lungs of male big blue mice following inhalation exposure to carcinogenic concentrations.

Ethylene oxide (EO) is a direct acting alkylating agent; in vitro and in vivo studies indicate that it is both a mutagen and a carcinogen. However, it remains unclear whether the mode of action (MOA) for cancer for EO is a mutagenic MOA, specifically via point mutation. To investigate the MOA for EO-induced mouse lung tumors, male Big Blue (BB) B6C3F1 mice (10/group) were exposed to EO by inhalation, 6 hr/day, 5 days/week for 4 (0, 10, 50, 100, or 200 ppm EO), 8, or 12 weeks (0, 100, or 200 ppm EO). Lung DNA samples were analyzed for cII mutant frequency (MF) at 4, 8 and 12 weeks of exposure; the mutation spectrum was analyzed for mutants from control and 200 ppm EO treatments. Although EO-induced cII MFs were 1.5- to 2.7-fold higher than the concurrent controls at 4 weeks, statistically significant increases in the cII MF were found only after 8 and 12 weeks of exposure and only at 200 ppm EO (P ≤ 0.05), which is twice the highest concentration used in the cancer bioassay. Consistent with the positive response, DNA sequencing of cII mutants showed a significant shift in the mutational spectra between control and 200 ppm EO following 8 and 12 week exposures (P ≤ 0.035), but not at 4 weeks. Thus, EO mutagenic activity in vivo was relatively weak and required higher than tumorigenic concentrations and longer than 4 weeks exposure durations. These data do not follow the classical patterns for a MOA mediated by point mutations. Environ. Mol. Mutagen. 58:122-134, 2017. © 2017 Wiley Periodicals, Inc.

Evaluation of cII gene mutation in the brains of Big Blue mice exposed to acrylamide and glycidamide in drinking water.

Potential health risks for humans from dietary exposure to acrylamide (AA) and its reactive epoxide metabolite, glycidamide (GA), exist because substantial amounts of AA are found in a variety of fried and baked starchy foods. AA is tumorigenic in rodents, and a large number of studies indicate that AA is genotoxic in multiple organs of mice and rats. Although AA is neurotoxic, there are no reports on AA-induced gene mutations in the mouse brain. Therefore, to investigate if gene mutation can be induced by AA or its metabolite GA, we screened brains for cII mutant frequency (MF) and scored for mutation types in previously treated male and female Big Blue mice with 0, 1.4 mM, and 7.0 mM AA or GA in drinking water for up to 4 weeks. High doses of AA and GA induced similar cII MFs in males and females but only the induced cII MF in males was significantly higher than the corresponding male control MF (p < 0.05). Molecular analysis of the cII mutants from males showed that AA and GA each induced at least a 2.5-fold increase in the incidence of G:C → T:A, A:T → T:A, and A:T → C:G transversions compared to the vehicle controls, with similar mutational spectra observed when comparing AA with GA treatment. These results suggest that the MFs and types of mutations induced by AA and GA in the brain are consistent with AA exerting its genotoxicity via metabolism to GA.

Development and validation of a new transgenic hairless albino mouse as a mutational model for potential assessment of photocarcinogenicity.

Short-term phototoxicity testing is useful in selecting test agents for the longer and more expensive photocarcinogenesis safety tests; however, no validated short-term tests have been proven reliable in predicting the outcome of a photocarcinogenesis safety test. A transgenic, hairless, albino (THA) mouse model was developed that carries the gpt and red/gam [Spi(-)] genes from the gpt delta mouse background and the phenotypes from the SKH-1 mouse background to use as a short-term test in lieu of photocarcinogenesis safety tests. Validation of the THA mouse model was confirmed by exposing groups of male mice to sub-erythemal doses of ultraviolet B (UVB) irradiation for three consecutive days emitted from calibrated overhead, Kodacel-filtered fluorescent lamps and measuring the mutant frequencies (MFs) in the gpt and red/gam (Spi(-)) genes and types of mutations in the gpt gene. The doses or irradiation were monitored with broad-spectrum dosimeters that were calibrated to a NIST-traceable standard and cumulative CIE-weighted doses were 20.55 and 41.0mJ/cm(2) (effective). Mice were sacrificed 14 days after the final UVB exposure and MFs in both the gpt and red/gam genes were evaluated in the epidermis. The exposure of mice to UVB induced significant ten- to twelve-fold increases in the gpt MF and three- to five-fold increases in the Spi(-) MF over their respective background MF, 26±3×10(-6) and 9±1×10(-6). The gpt mutation spectra were significantly different between that of the UVB-irradiated and that of non-irradiated mice although the mutation spectra of both groups were dominated by C→T transitions (84% and 66%). In mice exposed to UVB, the C→T transitions occurred almost exclusively at dipyrimidine sites (92%), whereas in non-irradiated control mice, the C→T transitions occurred at CpG sites (86%). These results suggest that the newly developed THA mice are a useful and reliable model for testing UVB-induced mutagenicity in skin tissue. The application of this model for short-term prediction of solar-induced skin carcinogenicity is presently under investigation.

Evaluation of cII mutations in lung of male Big Blue mice exposed by inhalation to vanadium pentoxide for up to 8 weeks.

Chronic inhalation of vanadium pentoxide (V2O5) increases the incidence of alveolar/bronchiolar tumors in male and female B6C3F1 mice at 1, 2, or 4 mg/m(3). The genotoxicity of V2O5 has been extensively investigated in the literature with mixed results. In general, tests for gene mutations have been negative. Both positive and negative results were reported for clastogenicity in vitro with some reports suggesting aneugenic potential. In vivo, V2O5 was negative in the mouse micronucleus test (erythrocyte) and comet assay (lung). Previously, K-ras mutations have been detected in the lung tumors in mice exposed to V2O5. Recently, a short-term inhalation study in B6C3F1 mice reported slight induction of 8-oxodGuo DNA lesions in lungs. Because 8-oxodGuo DNA lesions can lead to gene mutations if not repaired or if misrepaired, we have used groups of transgenic Big Blue (BB) mice (B6C3F1) to test whether V2O5 has mutagenic potential in vivo in the tumor target tissue under the conditions of the bioassay. Groups of six male BB mice were exposed to particulate aerosols containing 0, 0.1, or 1 mg/m(3) (tumorigenic concentration) V2O5 for 4 or 8 weeks (6h/day, 5 days/week) and cII mutant frequencies (MFs) were evaluated in the right lungs. A significant increase in lung weight was noted in mice exposed to 1 mg/m(3) V2O5 (P ≤ 0.05) compared to sham control, confirming exposure to an inflammatory level of the test material. The mean MFs (× 10(-6)) of mice in the 4-week exposure groups were 30 (sham control), 39 (0.1 mg/m(3)), and 24 (1 mg/m(3)) while the corresponding values in the 8-week exposure groups were 29, 48, and 17, respectively. None of these cII MFs measured at any time point was significantly higher than the corresponding control MFs (P ≥ 0.1). Overall, these results suggest that mutagenicity is not likely to be an initial key event in the lung tumorigenicity of V2O5.

Acrylamide-induced carcinogenicity in mouse lung involves mutagenicity: cII gene mutations in the lung of big blue mice exposed to acrylamide and glycidamide for up to 4 weeks.

Potential health risks for humans from exposure to acrylamide (AA) and its epoxide metabolite glycidamide (GA) have garnered much attention lately because substantial amounts of AA are present in a variety of fried and baked starchy foods. AA is tumorigenic in rodents, and a large number of in vitro and in vivo studies indicate that AA is genotoxic. A recent cancer bioassay on AA demonstrated that the lung was one of the target organs for tumor induction in mice; however, the mutagenicity of AA in this tissue is unclear. Therefore, to investigate whether or not gene mutation is involved in the etiology of AA- or GA-induced mouse lung carcinogenicity, we screened for cII mutant frequency (MF) in lungs from male and female Big Blue (BB) mice administered 0, 1.4, and 7.0 mM AA or GA in drinking water for up to 4 weeks (19-111 mg/kg bw/days). Both doses of AA and GA produced significant increases in cII MFs, with the high doses producing responses 2.7-5.6-fold higher than the corresponding controls (P ≤ 0.05; control MFs = 17.2 ± 2.2 and 15.8 ± 3.5 × 10(-6) in males and females, respectively). Molecular analysis of the mutants from high doses indicated that AA and GA produced similar mutation spectra and that these spectra were significantly different from the spectra in control mice (P ≤ 0.01). The predominant types of mutations in the lung cII gene from AA- and GA-treated mice were A:T → T:A, and G:C → C:G transversions, and -1/+1 frameshifts at a homopolymeric run of Gs. The MFs and types of mutations induced by AA and GA in the lung are consistent with AA exerting its genotoxicity via metabolism to GA. These results suggest that AA is a mutagenic carcinogen in mouse lungs and therefore further studies on its potential health risk to humans are warranted. Environ. Mol. Mutagen. 56:446-456, 2015. © 2015 Wiley Periodicals, Inc.

Temporal changes in K-ras mutant fraction in lung tissue of big blue B6C3F1 mice exposed to ethylene oxide.

Ethylene oxide (EO) is a genotoxicant and a mouse lung carcinogen, but whether EO is carcinogenic through a mutagenic mode of action remains unclear. To investigate this question, 8-week-old male Big Blue B6C3F1 mice (10 mice/group) were exposed to EO by inhalation-6 h/day, 5 days/week for 4 weeks (0, 10, 50, 100, or 200 ppm EO) and 8 or 12 weeks (0, 100, or 200 ppm EO). Lung DNA samples were analyzed for levels of 3 K-ras codon 12 mutations (GGT→GAT, GGT→GTT, and GGT→TGT) using ACB-PCR. No measureable level of K-ras codon 12 TGT mutation was detected (ie, all lung mutant fractions [MFs] ≤ 10⁻5). Four weeks of inhalation of 100 ppm EO caused a significant increase in K-ras codon 12 GGT→GTT MF relative to controls, whereas 50, 100, and 200 ppm EO caused significant increases in K-ras codon 12 GGT→GAT MF. In addition, significant inverse correlations were observed between K-ras codon 12 GGT→GTT MF and cII mutant frequency in the lungs of the same mice exposed to 50, 100, or 200 ppm EO for 4 weeks. Surprisingly, 8 weeks of exposure to 100 and 200 ppm EO caused significant decreases in K-ras MFs relative to controls. Thus, the changes in K-ras MF as a function of cumulative EO dose were nonmonotonic and were consistent with EO causing early amplification of preexisting K-ras mutations, rather than induction of K-ras mutation through genotoxicity at codon 12. The possibility that these changes reflect K-ras mutant cell selection under varying degrees of oxidative stress is discussed.

In vivo cII, gpt, and Spi⁻ gene mutation assays in transgenic mice and rats.

Transgenic mutation assays are used to identify and characterize genotoxic hazards and for determining the mode of action for carcinogens. The three most popular transgenic mutational models are Big Blue® (rats or mice), Muta™ mouse (mice), and gpt-delta (rats or mice). The Big Blue® and Muta™ mouse models use the cII gene as a reporter of mutation whereas gpt-delta rodents use the gpt gene and the red/gam genes (Spi⁻ selection) as mutation reporter genes. Here we describe methodology for conducting mutation assays with these transgenes. Transgenes recovered from tissue DNA are packaged into infectious lambda phage, bacteria are infected with the phage, and cII-mutant and Spi⁻ plaques and gpt-mutant colonies are isolated using selective conditions and quantified. Selected mutants can be further analyzed for identification of small sequence alterations in the cII and gpt genes and large deletions at the Spi⁻ locus.

Mutagenicity of acrylamide and glycidamide in the testes of big blue mice.

Acrylamide (AA) is an industrial chemical, a by-product of fried starchy foods, and a mutagen and rodent carcinogen. It can also cause damage during spermatogenesis. In this study, we investigated whether AA and its metabolite glycidamide (GA) induce mutagenic effects in the germ cells of male mice. Male Big Blue transgenic mice were administered 1.4 or 7.0mM of AA or GA in the drinking water for up to 4 weeks. Testicular cII mutant frequency (MF) was determined 3 weeks after the last treatment, and the types of the mutations in the cII gene were analyzed by DNA sequencing. The testes cII MFs in mice treated with either the low or high exposure concentrations of AA and GA were increased significantly. There was no significant difference in the cII MFs between AA and GA at the low exposure concentration. The mutation spectra in mice treated with AA (1.4mM) or GA (both 1.4 and 7.0mM) differed significantly from those of controls, but there were no significant differences in mutation patterns between AA and GA treatments. Comparison of the mutation spectra between testes and livers showed that the spectra differed significantly between the two tissues following treatment with AA or GA, whereas the mutation spectra in the two tissues from control mice were similar. These results suggest that AA possesses mutagenic effects on testes by virtue of its metabolism to GA, possibly targeting spermatogonial stem cells, but possibly via different pathways when compared mutations in liver.

The genotoxicity of acrylamide and glycidamide in big blue rats.

Acrylamide (AA), a mutagen and rodent carcinogen, recently has been detected in fried and baked starchy foods, a finding that has prompted renewed interest in its potential for toxicity in humans. In the present study, we exposed Big Blue rats to the equivalent of approximately 5 and 10 mg/kg body weight/day of AA or its epoxide metabolite glycidamide (GA) via the drinking water, an AA treatment regimen comparable to those used to produce cancer in rats. After 2 months of dosing, the rats were euthanized and blood was taken for the micronucleus assay; spleens for the lymphocyte Hprt mutant assay; and liver, thyroid, bone marrow, testis (from males), and mammary gland (females) for the cII mutant assay. Neither AA nor GA increased the frequency of micronucleated reticulocytes. In contrast, both compounds produced small (approximately twofold to threefold above background) but significant increases in lymphocyte Hprt mutant frequency (MF, p < 0.05), with the increases having dose-related linear trends (p < 0.05 to p < 0.001). Neither compound increased the cII MF in testis, mammary gland (tumor target tissues), or liver (nontarget tissue), while both compounds induced weak positive increases in bone marrow (nontarget tissue) and thyroid (target tissue). Although the genotoxicity in tumor target tissue was weak, in combination with the responses in surrogate tissues, the results are consistent with AA being a gene mutagen in the rat via metabolism to GA.

Evaluation of mutagenic mode of action in Big Blue mice fed methylphenidate for 24 weeks.

Methylphenidate hydrochloride (MPH), a widely prescribed pediatric drug for attention deficit hyperactivity disorder, induced liver adenocarcinomas in B6C3F1 mice exposed to 500 ppm in feed for 2 years (Dunnick and Hailey (1995) [14]). In order to determine if the induction of liver tumors was by a mutagenic mode of action, groups of male Big Blue (BB) mice (B6C3F1 background) were fed diets containing 50-4000 ppm MPH for 4, 12, or 24 weeks. At sacrifice, the livers were removed and the cII mutant frequency (MF) and spectrum of cII mutations were determined. In addition, the frequencies of micronucleated reticulocytes (MN-RETs) and normochromatic erythrocytes (MN-NCEs) were measured in peripheral blood erythrocytes as was the Hprt MF in splenic lymphocytes. Food consumption and body weight gain/loss were recorded weekly for each animal. The levels of MPH and RA were determined immediately before sacrifice in the serum of mice fed MPH for 24 weeks. A significant loss in body weights (p

The genetic toxicology of methylphenidate hydrochloride in non-human primates.

The studies presented in this work were designed to evaluate the genetic toxicity of methylphenidate hydrochloride (MPH) in non-human primates (NHP) using a long-term, chronic dosing regimen. Thus, approximately two-year old, male rhesus monkeys of Indian origin were orally exposed to MPH diluted in the electrolyte replenisher, Prang, five days per week over a 20-month period. There were 10 animals per dose group and the doses were (1) control, Prang only, (2) low, 0.15 mg/kg of MPH twice per day increased to 2.5mg/kg twice per day and (3) high, 1.5 mg/kg of MPH twice per day increased to 12.5 mg/kg twice per day. Blood samples were obtained from each animal to determine the base-line serum levels of MPH and the major metabolite of MPH in NHP, ritalinic acid (RA). In addition, the base-line frequency of micronucleated erythrocytes (MN-RETs) by flow cytometry, HPRT mutants by a lymphocyte cloning assay, and chromosome aberrations by FISH painting were determined from peripheral blood samples. Once dosing began, the serum levels of MPH and its major metabolite, RA, were determined monthly. The MN-RET frequency and health parameters (CBC, serum chemistries) were also determined monthly. HPRT mutant and chromosome aberration frequencies were measured every three months. CBC values and serum chemistries, with the exception of alanine amino transferase, were within normal limits over the course of drug exposure. The final plasma levels of MPH were similar to those produced by the pediatric dose of 0.3 microg/ml. No significant increases in the frequencies of MN-RETs, HPRT mutants, or chromosome aberrations were detected in the treated animals compared to the control animals over the 20-month exposure period.

Pharmacokinetics, dose-range, and mutagenicity studies of methylphenidate hydrochloride in B6C3F1 mice.

Methylphenidate hydrochloride (MPH) is one of the most frequently prescribed pediatric drugs for the treatment of attention deficit hyperactivity disorder. In a recent study, increased hepatic adenomas were observed in B6C3F1 mice treated with MPH in their diet. To evaluate the reactive metabolite, ritalinic acid (RA) of MPH and its mode of action in mice, we conducted extensive investigations on the pharmacokinetics (PK) and genotoxicity of the drug in B6C3F1 mice. For the PK study, male B6C3F1 mice were gavaged once with 3 mg/kg body weight (BW) of MPH and groups of mice were sacrificed at various time points (0.25-24 hr) for serum analysis of MPH and RA concentrations. Groups of male B6C3F1 mice were fed diets containing 0, 250, 500, 1,000, 2,000, or 4,000 ppm of MPH for 28 days to determine the appropriate doses for 24-week transgenic mutation studies. Also, the micronucleus frequencies (MN-RETs and MN-NCEs), and the lymphocyte Hprt mutants were determined in peripheral blood and splenic lymphocytes, respectively. Mice fed 4,000 ppm of MPH lost significant BW compared to control mice (P < 0.01). There was a significant increase in the average liver weights whereas kidneys, seminal vesicle, testes, thymus, and urinary bladder weights of mice fed higher doses of MPH were significantly lower than the control group (P < or = 0.05). There was no significant increase in either the Hprt mutant frequency or the micronucleus frequency in the treated animals. These results indicated that although MPH induced liver hypertrophy in mice, no genotoxicity was observed.

Genotoxicity of acrylamide and its metabolite glycidamide administered in drinking water to male and female Big Blue mice.

The recent discovery of acrylamide (AA), a probable human carcinogen, in a variety of fried and baked starchy foods has drawn attention to its genotoxicity and carcinogenicity. Evidence suggests that glycidamide (GA), the epoxide metabolite of AA, is responsible for the genotoxic effects of AA. To investigate the in vivo genotoxicity of AA, groups of male and female Big Blue (BB) mice were administered 0, 100, or 500 mg/l of AA or equimolar doses of GA, in drinking water, for 3-4 weeks. Micronucleated reticulocytes (MN-RETs) were assessed in peripheral blood within 24 hr of the last treatment, and lymphocyte Hprt and liver cII mutagenesis assays were conducted 21 days following the last treatment. Further, the types of cII mutations induced by AA and GA in the liver were determined by sequence analysis. The frequency of MN-RETs was increased 1.7-3.3-fold in males treated with the high doses of AA and GA (P < or = 0.05; control frequency = 0.28%). Both doses of AA and GA produced increased lymphocyte Hprt mutant frequencies (MFs), with the high doses producing responses 16-25-fold higher than that of the respective control (P < or = 0.01; control MFs = 1.5 +/- 0.3 x 10(-6) and 2.2 +/- 0.5 x 10(-6) in females and males, respectively). Also, the high doses of AA and GA produced significant 2-2.5-fold increases in liver cII MFs (P < or = 0.05; control MFs = 26.5 +/- 3.1 x 10(-6) and 28.4 +/- 4.5 x 10(-6)). Molecular analysis of the mutants indicated that AA and GA produced similar mutation spectra and that these spectra were significantly different from that of control mutants (P < or = 0.001). The predominant types of mutations in the liver cII gene from AA- and GA-treated mice were G:C-->T:A transversions and -1/+1 frameshifts in a homopolymeric run of Gs. The results indicate that both AA and GA are genotoxic in mice. The MFs and types of mutations induced by AA and GA in the liver are consistent with AA exerting its genotoxicity in BB mice via metabolism to GA.

Effects of daidzein, genistein, and 17beta-estradiol on 7,12-dimethylbenz[a]anthracene-induced mutagenicity and uterine dysplasia in ovariectomized rats.

Phytoestrogens, primarily isoflavones daidzein (DZ) and genistein (GE), are increasingly used by postmenopausal women as an alternative to hormone replacement therapy due to reports that estrogen therapy increases the risk of breast and endometrial cancers. These compounds, as estrogen receptor agonists, may influence chemical carcinogenesis in estrogen-responsive tissues such as the uterus. We utilized ovariectomized (OVX) rats to model menopause and assessed the effects of dietary DZ, GE, or 17beta-estradiol (E2) on carcinogen-induced mutagenesis and carcinogenesis in the rat uterus. Big Blue transgenic rats (derived from Fischer 344 strain) were exposed to 7,12-dimethylbenz[a]anthracene (DMBA) in the presence or absence of the supplements. At 16- or 20-wk sacrifice, the uteri were removed and processed to determine mutant frequencies (MFs) and immunohistochemical or histopathological parameters, respectively. In rats treated with DMBA alone, a significant increase in lacI MFs (P < 0.01) in both OVX and intact (INT) rats was observed. The DMBA-induced MFs were not significantly altered by dietary DZ, GE, or E2 in both OVX and INT rats. Although dysplasia was not induced in the uterus of OVX and INT rats treated with DMBA alone, it was detected in 55% of OVX rats fed E2 alone and in 100% of OVX rats fed E2 along with DMBA exposure. Cell proliferation also was significantly higher in OVX rats fed E2 and treated with DMBA. In rats fed the isoflavones and treated with DMBA, the incidence of dysplasia was either reduced or virtually absent in both OVX and INT groups. These results indicate that a high incidence of dysplasia was associated with E2 feeding with or without DMBA treatment in the OVX rats, whereas the incidence was low in rats fed DZ or GE and treated with DMBA, suggesting a weak estrogen receptor agonist of DZ or GE in the rat uterus. The absence of dysplasia in OVX rats exposed to DMBA alone also suggests, in part, a promotional mechanism via estrogen- or isoflavone-driven cell proliferation.

17 Beta-estradiol and not genistein modulates lacI mutant frequency and types of mutation induced in the heart of ovariectomized big blue rats treated with 7, 12-dimethylbenz[a]anthracene.

In industrialized countries, heart disease rates are higher among women after menopause. Recent studies indicate that consumption of phytoestorogens, e.g., isoflavones such as genistein (GE), may have potential cardiovascular health benefits; however, no studies have evaluated the effect of these agents on toxicant-induced damage in the heart. Since estrogen receptors are found in the heart, and GE mimics estrogenic effects, we have examined whether or not dietary GE or 17 beta-estradiol (E2) modulates the lacI mutant frequency (MF) in the heart of ovariectomized (OVX) Big Blue rats exposed to the model carcinogen 7,12-dimethylbenz[a]anthracene (DMBA). Groups of female rats were administered 80 mg/kg DMBA or vehicle by gavage and were chronically fed with diets containing 0, 250, or 1,000 microg/g GE or 5 microg/g E2. Sixteen weeks after carcinogen treatment, the animals were sacrificed and the hearts were removed and processed for determining the frequency and types of mutations in the heart tissue. GE and E2 supplementation alone resulted in nonsignificant increases in MF. The DMBA-induced lacI MF in the heart was sevenfold higher than the control (119.8 +/- 18.7 x 10(-6) vs. 17.4 +/- 3.2 x 10(-6); P < 0.001). GE in the diet had no significant effect on DMBA mutagenicity, while feeding E2 to DMBA-treated rats caused a significant reduction in the MF (119.8+/- 18.7 x 10(-6) vs. 61.4 +/- 13.5 x 10(-6); P < 0.017). DNA sequence analysis revealed that the majority of DMBA-induced mutations in rats fed control diet were A:T-->T:A (42%) and G:C-->T:A (19%) transversions, followed by G:C-->A:T (13%) and A:T-->G:C (8%) transitions. Feeding E2 altered the DMBA-induced mutational spectra by decreasing A:T-->T:A (23%) and G:C-->T:A (13%) transversions and increasing G:C-->A:T (24%) and A:T-->G:C (21%) transitions. Taken together, the results suggest that DMBA can induce gene mutations in heart tissue of OVX rats, and while dietary GE had little or no effect on DMBA-induced mutation, dietary E2 reduced the mutagenicity of DMBA.

Mutations induced by alpha-hydroxytamoxifen in the lacI and cII genes of Big Blue transgenic rats.

The antiestrogen tamoxifen is widely used for the treatment of breast cancer and more recently for the prevention of breast cancer. A concern over the use of tamoxifen as a chemopreventive agent is its carcinogenicity in rat liver, through a genotoxic mechanism involving alpha-hydroxylation, esterification, and DNA adduct formation, primarily by reaction with dG. In a recent study [Gamboa da Costa et al., Cancer Lett., 176, 37-45 (2002)], we demonstrated a significant increase in the mutant frequency in the lacI gene of Big Blue rats treated with tamoxifen, and a further increase in rats administered alpha-hydroxytamoxifen. In the present study, we have assessed mutation induction by tamoxifen and alpha-hydroxytamoxifen in the liver cII gene of Big Blue rats and have characterized the types of mutations induced by alpha-hydroxytamoxifen in the liver lacI and cII genes. The mutant frequencies in the liver cII gene were 80 +/- 13 x 10(-6) in the control, 112 +/- 13 x 10(-6) in the tamoxifen-treated group (P < 0.01 vs. control), and 942 +/- 114 x 10(-6) in the alpha-hydroxytamoxifen-treated animals (P < 0.001 vs. control; P < 0.001 vs. tamoxifen). Molecular analysis of the mutants indicated that the alpha-hydroxytamoxifen-induced mutational spectrum differed significantly from the control spectrum, but was very similar to the spectrum induced by tamoxifen for both the lacI and cII genes [Davies et al., ENVIRON: Mol. Mutagen., 28, 430-433 (1996); Davies et al., Carcinogenesis, 20, 1351-1356 (1999)]. G:C --> T:A transversion was the major type of mutation induced by alpha-hydroxytamoxifen and tamoxifen, while G:C --> A:T transition was the main type of mutation in the control. These results support the hypothesis that alpha-hydroxytamoxifen is a major proximate tamoxifen metabolite causing the initiation of tumors in the liver of rats treated with tamoxifen.