Sharon D. Shelton

Mutagenicity and carcinogenicity in relation to DNA adduct formation in rats fed leucomalachite green

Leucomalachite green is a persistent and prevalent metabolite of malachite green, a triphenylmethane dye that has been used widely as an antifungal agent in the fish industry. Concern over the use of malachite green is due to the potential for consumer exposure, evidence suggestive of tumor promotion in rodent liver, and suspicion of carcinogenicity based on structure-activity relationships. Our previous study indicated that feeding rodents malachite or leucomalachite green resulted in a dose-related increase in liver DNA adducts, and that, in general, exposure to leucomalachite green caused an increase in the number and severity of changes greater than was observed following exposure to malachite green. To characterize better the genotoxicity of leucomalachite green, female Big Blue rats were fed leucomalachite green at doses of 0, 9, 27, 91, 272, or 543 ppm for up to 32 weeks. The livers were analyzed for lacI mutations at 4, 16, and 32 weeks and DNA adducts at 4 weeks. Using a 32P-postlabeling assay, we observed a dose-related DNA adduct in the livers of rats fed 91, 272, and 543 ppm leucomalachite green. A approximately 3-fold increase in lacI mutant frequency was found in the livers of rats fed 543 ppm leucomalachite green for 16 weeks, but significant increases in mutant frequencies were not found for any of the other doses or time points assayed. We also conducted 2-year tumorigenesis bioassays in female and male F344 rats using 0, 91, 272, and 543 ppm leucomalachite green. Preliminary results indicate an increasing dose trend in lung adenomas in male rats treated with leucomalachite green, but no increase in the incidence of liver tumors in either sex of rat. These results suggest that the DNA adduct formed in the livers of rats fed leucomalachite green has little mutagenic or carcinogenic consequence.

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.

Comparison of in vivo mutagenesis in the endogenous Hprt gene and the lacI transgene of Big Blue® rats treated with 7,12-dimethylbenz[a]anthracene

The lacI transgene of Big Blue(R) (BB) rats was evaluated as a reporter of in vivo mutation by comparing mutant frequencies (MFs) in it and in the endogenous Hprt gene. Seven-week old female BB rats were given single doses of 0, 20, 75 and 130 mg/kg of 7, 12-dimethylbenz(a)anthracene (DMBA) by gavage, and Hprt and lacI MFs in splenic lymphocytes were measured over a period of 18 weeks. The Hprt MFs in treated rats increased for 10 weeks and then declined; 130 mg/kg of DMBA produced a maximum Hprt MF of 168+/-11.4x10-6 clonable lymphocytes, while the MF in control rats was 7.4+/-1. 5x10-6. DMBA exposure of generic F344 rats resulted in a similar time-course of mutant induction but produced about 50% higher Hprt MFs with the 75 and 130 mg/kg doses. In contrast, the lacI MFs increased for 6 weeks and then remained relatively constant; 130 mg/kg of DMBA produced a maximum increase in lacI MF of 341+/-83x10-6 PFU compared with 25+/-5x10-6 PFU in control rats. The Hprt mutant frequencies in DMBA-treated BB and F344 rats were significantly increased over control values for every dose-time combination examined, while only the 130 mg/kg dose consistently produced lacI MFs that were significantly above the controls. In addition, the fold-increase in MF for treated vs. control rats was two times higher for the Hprt gene than the lacI gene due to the higher MFs in the lacI gene of control rats. Differences between the lacI and Hprt genes in the kinetics of mutant induction, in the frequency of induced mutants, and in the sensitivity of mutant detection could be explained at least partially by the properties of these two genes.

Comparison of the types of mutations induced by 7,12-dimethylbenz[a]anthracene in the lacI and hprt genes of Big Blue rats.

An important question regarding the use of transgenic reporter genes to detect mutation in rodents is how the types of mutations recovered in transgenes compare with the types of mutations found in the endogenous genes. In this study, we examined mutations induced by 7,12‐dimethylbenz‐[a]anthracene in the lacI transgene and the endogenous hprt gene of lymphocytes from Big Blue® rats and in the hprt gene of lymphocytes from non‐transgenic Fischer 344 rats. The overall mutation profiles found in these genes were remarkably similar: the majority of mutations were base pair substitutions, with the most common mutation being A:T → T:A transversion. Differences were found for the mutational profiles endogenous gene and transgene with respect to the location of the mutations and the orientation of basepair substitutions in the DNA strands. In most cases, these differences could be explained by the nature of the target genes. The results support the use of the lacI transgene for detecting in vivo mutation. Environ. Mol. Mutagen. 31:149–156, 1998 Published 1998 Wiley‐Liss, Inc. This article is a US Government work and, as such, is in the public domain in the United States of America.

Comparison of mutant frequencies and types of mutations induced by thiotepa in the endogenous Hprt gene and transgenic lacI gene of Big Blue® rats

The utility of the lacI transgene of Big Blue rats as a reporter of in vivo mutation was evaluated by comparing the frequency and types of mutations induced by thiotepa in the transgene and the endogenous Hprt gene. Transgenic rats were given i.p. injections of 1.4 mg/kg of thiotepa three times per week over a period of 4 weeks (a total dose of 16.8 mg/kg); 1 week after the last injection, mutation assays were performed on spleen lymphocytes isolated from the animals. Thiotepa treatment increased the lacI mutant frequency from 34.8 +/- 4.1 x 10(-6) in control animals to 140.9 +/- 64.8 x 10(-6) (p = 0.0020) and the Hprt mutant frequency from 3.5 +/- 1.5 x 10(-6) to 41.1 +/- 23.2 x 10(-6) (p = 0.0028). Sequence analysis of lacI mutant DNA and Hprt mutant cDNA produced similar overall mutation patterns: G:C-->T:A transversion was the most common base pair substitution (32% of independent mutations in the lacI gene and 28% of Hprt mutations), and deletions and insertions accounted for 34% of mutations in the lacI gene and 28% in the Hprt gene. The majority of thiotepa-induced base pair substitutions in the Hprt gene occurred with the mutated purine on the non-transcribed DNA strand, while no strand-related bias was found for mutations in the lacI gene. Substitutions at G:C base pairs in the lacI gene, but not in the Hprt gene, were found disproportionately in CpG sites. In addition, multiplex polymerase chain reaction analysis of genomic DNA from the Hprt mutants indicated that 34% had relatively large deletions; none of these deletions was detected by the cDNA analysis. The results indicate that the frequency of thiotepa-induced mutants in Big Blue rats was 2.8-fold greater in the lacI gene than in the Hprt gene. Although the Hprt gene recovered a fraction of large deletions not found among the lacI mutants, the effects of transcription-coupled DNA repair in the Hprt gene and the targeting of base pair substitutions to G:C base pairs in CpG sites may have contributed to the higher mutant frequencies induced by thiotepa in the lacI transgene compared with the Hprt gene.

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 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 ≤ 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. Environ. Mol. Mutagen., 2008. Published 2008 Wiley‐Liss, Inc.

Mutant frequency and molecular analysis of in vivo lacI mutations in the bone marrow of Big Blue rats treated with 7, 12-dimethylbenz[a]anthracene.

Recently, we evaluated lacI mutations in lymphocytes and mammary tissue of Big Blue (BB) rats exposed to 7,12‐dimethylbenz[a]anthracene (DMBA). The results on the time course of mutant induction suggested that the lacI gene may manifest a tissue‐specific increase in mutant frequency (MF). To test whether a tissue‐specific increase in lacI MF is dependent on the cell proliferation rate of a tissue, we examined rapidly proliferating bone marrow cells for DMBA‐induced lacI mutations. Seven‐week‐old female BB rats were given single doses of 0, 20, and 130 mg/kg DMBA by gavage and the lacI MFs in the bone marrow were measured over a period of 14 weeks following treatment. Bone marrow cells had a remarkably low average background MF (3.1 ± 1.6 × 10−6 plaque‐forming units) and the DMBA‐induced lacI MFs were significantly higher than control MFs for both doses and at all time points (P < 0.01). The lacI MF in the bone marrow increased for 2 weeks and then remained relatively constant; 20 and 130 mg/kg DMBA produced 34‐ and 106‐fold increases in MF over control MF. DNA sequencing revealed that the majority of DMBA‐induced lacI mutations were base‐pair substitutions and that A:T → T:A (48%) and G:C → T:A (24%) transversions were the predominant types. Thus, the different lacI mutation fixation times observed for bone marrow (2 weeks), mammary (10 weeks), and lymphocytes (6 weeks) suggest that the lacI gene manifests a tissue‐specific mutation fixation time, which may depend on the cell proliferation rate of a tissue. In addition, the relatively low spontaneous MF in bone marrow compared with that in other tissues may be useful for increasing the sensitivity of the assay for detecting induced MFs in BB rats. Environ. Mol. Mutagen. 36:235–242, 2000. Published 2000 Wiley‐Liss, 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.