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L Recio

Publications and source records attributed to L Recio.

At least 19 recordsLinked to original sources

Absence of acrylamide-induced genotoxicity in CYP2E1-null mice: evidence consistent with a glycidamide-mediated effect.

Acrylamide, an animal carcinogen and germ cell mutagen present at low (ppm) levels in heated carbohydrate-containing foodstuffs, is oxidized by cytochrome P4502E1 (CYP2E1) to the epoxide glycidamide, which is believed to be responsible for the mutagenic and carcinogenic activity of acrylamide. We recently reported a comparison of the effects of acrylamide on the genetic integrity of germ cells of male wild-type and CYP2E1-null mice [B.I. Ghanayem, K.L. Witt, L. El-Hadri, U. Hoffler, G.E. Kissling, M.D. Shelby, J.B. Bishop, Comparison of germ-cell mutagenicity in male CYP2E1-null and wild-type mice treated with acrylamide: evidence supporting a glycidamide-mediated effect, Biol. Reprod. 72 (2005) 157-163]. In those experiments, dose-related increases in dominant lethal mutations were detected in uterine contents of female mice mated to acrylamide-treated wild-type males but not CYP2E1-null males, clearly implicating CYP2E1-mediated formation of glycidamide in the induction of genetic damage in male germ cells. We hypothesized that acrylamide-induced somatic cell damage is also caused by glycidamide. Therefore, to examine this hypothesis, female wild-type and CYP2E1-null mice were administered acrylamide (0, 25, 50mg/kg) by intraperitoneal injection once daily for 5 consecutive days. Twenty-four hours after the final treatment, blood and tissue samples were collected. Erythrocyte micronucleus frequencies were determined using flow cytometry and DNA damage was assessed in leukocytes, liver, and lung using the alkaline (pH>13) single cell gel electrophoresis (Comet) assay. Results were consistent with the earlier observations in male germ cells: significant dose-related increases in micronucleated erythrocytes and DNA damage in somatic cells were induced in acrylamide-treated wild-type but not in the CYP2E1-null mice. These results support the hypothesis that genetic damage in somatic and germ cells of mice-treated with acrylamide is dependent upon metabolism of the parent compound by CYP2E1. This dependency on metabolism has implications for the assessment of human risks resulting from occupational or dietary exposure to acrylamide. CYP2E1 polymorphisms and variability in CYP2E1 activity associated with, for example, diabetes, obesity, starvation, and alcohol consumption, may result in altered metabolic efficiencies leading to differential susceptibilities to acrylamide toxicities in humans.

Acrylamides↗

Transgenic tumor models for carcinogen identification: the heterozygous Trp53-deficient and RasH2 mouse lines.

Genetically altered mouse models (GAMM) for human cancers have been critical to the investigation and characterization of oncogene and tumor suppressor gene expression and function and the associated cancer phenotype. Similarly, several of the mouse models with defined genetic alterations have shown promise for identification of potential human carcinogens and investigation of mechanisms of carcinogen-gene interactions and tumorigenesis. In particular, both the B6.129N5-Trp53 mouse, heterozygous for a p53 null allele, and the CB6F1-RasH2 mouse, hemizygous for the human H-ras transgene, have been extensively investigated. Using 26-week exposure protocols at or approaching the maximum tolerated dose, the summary results to date indicate the potential for GAMM to identify and, possibly, classify chemicals of potential risk to humans using short-term carcinogenicity experiments. This IWGT session focused on: (1) the development of recommendations for genetic/molecular characterization required in animals, tissues, and tumors before and after treatment for identification of presumptive human carcinogens based on the current state of knowledge, (2) identification of data gaps in our current state of knowledge, and (3) development of recommendations for research strategies for further development of our knowledge base of these particular models. By optimization of protocols and identification of significant outcomes and responses to chemical exposure in appropriate short-term mechanism-based genetically altered rodent models, strategies for prevention and intervention may be developed and employed to the benefit of public health.

Animals↗

Mutational spectrum of 1,3-butadiene and metabolites 1,2-epoxybutene and 1,2,3,4-diepoxybutane to assess mutagenic mechanisms.

1,3-Butadiene (BD) is a multisite carcinogen and is mutagenic in multiple tissues of B6C3F1 mice. BD is bioactivated to at least three directly mutagenic metabolites: 1,2-epoxybutene (EB), 1,2-epoxy-3,4-butanediol (EBD), and 1,2,3,4-diepoxybutane (DEB). However, the contribution of these individual metabolites to the carcinogenicity and in vivo mutatidnal spectrum of BD is uncertain. To assess the role of two BD metabolites EB and DEB in the in vivo mutagenicity of the parent compound BD, we examined the in vitro mutational spectra of EB and DEB in human and rodent cells. We also examined the in vivo mutagenicity and mutational spectrum of inhaled EB in the lung. In the bone marrow and spleen of B6C3F1 laci transgenic mice, BD-induced an increased frequency of the identical class of point mutations at A:T base pairs: AT-->GC transitions and AT-->TA transversions. BD exposure also induced an increased frequency of GC-->AT transitions in the spleen that was not observed in bone marrow, demonstrating tissue-specific differences in mutation spectrum. Exposure of Rat2 laci transgenic cells and human TK6 lymphoblasts to EB-induced an increased frequency of AT-->TA transversions. DEB exposure induced an increased frequency of AT-->TA transversions and partial deletions at hprt in human cells. In Rat laci transgenic cells, DEB was not mutagenic at laci but induced an increased frequency of micronuclei. In contrast to inhaled BD, inhaled DEB and EB were not mutagenic in the bone marrow or spleen. However, EB was mutagenic in the lungs. In the lung of mice, EB-induced specific increases in GC-->AT transitions, AT-->TA transversions, and deletion events. AT-->TA transversions are the most consistent mutation observed across biological systems following in vivo exposure to BD or in vitro exposures to EB and DEB. Although, BD exposure in mice induces chromosomal alterations and single base substitutions, the specific BD metabolite that induces the genetic events leading to tumors is uncertain. At present, it appears that only DEB can effectively induce this range of mutagenic events at levels of this metabolite that occur in the blood of mice exposed to BD. Detailed investigations to identify relevant biomarkers of BD exposure and response, particularly DNA adducts or lesions, that can be biologically linked to the range of genotoxic events known to occur in mice exposed to BD are needed.

Air Pollutants↗

Lung-specific mutagenicity and mutational spectrum in B6C3F1 lacI transgenic mice following inhalation exposure to 1,2-epoxybutene.

1,3-Butadiene (BD) is carcinogenic and mutagenic in B6C3F1 mice. BD inhalation induces an increased frequency of specific base substitution mutations in the bone marrow and spleen of B6C3F1 lacI transgenic mice. BD is bioactivated to at least three mutagenic metabolites: 1,2-epoxybutene (EB), 1,2-epoxy-3,4-butanediol (EBD), and 1,2,3,4-diepoxybutane (DEB), however, the contribution of these individual metabolites to the in vivo mutational spectrum of BD is uncertain. In the present study, lacI transgenic mice were exposed by inhalation (6h per day, 5 days per week for 2 weeks) to 0 or 29.9ppm of the BD metabolite, EB to assess its contribution to the in vivo mutational spectrum of BD. No increase in lacI mutant frequency was observed in the bone marrow or spleen of EB-exposed mice. The lack of mutagenicity in the bone marrow or spleen likely relate to insufficient levels of EB reaching these tissues. The lacI mutant frequency was increased 2.7-fold in the lungs of EB-exposed mice (mean+/-S.D., 9.9+/-3.0x10(-5)) compared to air control mice (3.6+/-0.7x10(-5)). DNA sequence analysis of 65 and 66 mutants from the lungs of air control and EB-exposed mice, respectively, revealed an increase in the frequency of two categories of base substitution mutation and deletions. Like mice exposed to BD, EB-exposed mice had an increased frequency of A:T-->T:A transversions. However, in contrast to the BD mutational spectra, G:C-->A:T transitions at 5'-CpG-3' sequences, occurred with increased frequency in the EB-exposed mice. The increased frequency of deletions as well as the induction of two tandem mutations and a tandem deletion in the lungs of EB-exposed mice are also inconsistent with previous mutational spectra from BD-exposed mice or EB-exposed cells in culture. We hypothesize that the direct in vivo mutagenicity and further in situ metabolism of EB in the lungs of EB-exposed mice played a prominent role in the generation of the current mutational spectrum.

Administration, Inhalation↗

Is p53 haploinsufficient for tumor suppression? Implications for the p53+/- mouse model in carcinogenicity testing.

The p53 tumor suppressor gene has been shown to be critical in preventing cancer in humans and mice. We have generated and extensively characterized p53-deficient mice lacking one (p53+/-) or both (p53-/-) p53 alleles. The p53-deficient mice are much more susceptible to an array of different tumor types than their wild-type (p53+/+) littermates. The enhanced tumor susceptibility of the p53+/- mice has made them one of several transgenic mouse models that are being considered as substitutes for standard 2-year rodent carcinogenicity assays. In order to fully exploit this model, it will be important to understand some of the basic biological and molecular mechanisms that underlie its enhanced tumor susceptibility. With this in mind, we have explored the fate of the remaining wild-type p53 allele in spontaneously arising p53+/- tumors and have shown that over half of these tumors retain an intact, functional wild-type p53 allele. This suggests that p53 is haploinsufficient for tumor suppression and that mere reduction in p53 dosage is sufficient to promote cancer formation. To support the idea that p53 is indeed a haploinsufficient tumor suppressor, we show here that normal p53+/- cells exhibit reduced parameters of growth control and stress response compared to their p53+/- counterparts. We hypothesize that the reduced p53 dosage in the p53+/- cells provides an environment more conducive to the development of further oncogenic lesions and the initiation of a tumor. Finally, we have assessed p53 loss of heterozygosity (LOH) in carcinogen-induced p53+/- tumors and have found that some agents induce tumors that almost invariably exhibit p53 LOH, whereas other agents induce tumors that often retain the wild-type p53 allele. Our preliminary data suggest that LOH is dependent on both the mechanism of genotoxicity of the agent utilized and the tissue type targeted.

Animal Testing Alternatives↗

Induction and time-dependent accumulation of micronuclei in peripheral blood of transgenic p53+/- mice, Tg.AC (v-Ha-ras) and parental wild-type (C57BL/6 and FVB/N) mice exposed to benzene by inhalation.

In this study, we determined the induction and time-dependent accumulation of micronuclei in the peripheral blood of transgenic C57BL/6 p53+/- mice (p53+/- mice), FVB/N Tg.AC v-Ha-ras mice (Tg.AC mice) and their isogenic parental strains, FVB/N and C57BL/6 following inhalation exposure to benzene. Our objective was to determine the impact of p53 heterozygosity in p53+/- mice and the v-Ha-ras transgene in Tg.AC mice on micronuclei induction following exposure to inhaled benzene. A flow cytometric technique that distinguishes micronucleated red blood cells (MN-RBC) from micronucleated reticulocytes (MN-RET) was used. Mice were exposed to 0, 100 or 200 p.p.m. benzene using three different exposure regimens that resulted in an equal weekly cumulative exposure (3000 p.p.m.x hours) to benezene: 100 p.p.m. for 6 h/day, 5 days/week, Monday to Friday (M-F); 100 p.p.m. for 10 h/day, 3 days/week, Monday, Wednesday, Friday (MWF); and 200 p.p.m. for 5 h/day, 3 days/week MWF. Significant elevations of MN-RBC and MN-RET were observed from 1 week exposure in all of the benzene-exposed groups that increased in a time-dependent manner for up to 13 weeks exposure. Fewer MN-RBC and MN-RET were induced in the 200 p.p.m. benzene exposure group than in mice exposed to 100 p.p.m. The reduction in the frequency of MN-RBC in the 200 p.p.m.x5 h benzene exposure group is probably due to metabolic saturation resulting in a lower bone marrow dose (concentration x time) than in the 100 p.p.m. exposure groups. No differences were observed in the frequency of MN-RBC or MN-RET in Tg.AC compared with the FVB/N isogenic controls. At certain time points the frequency of micronuclei was less in the heterozygous p53+/- mice than determined in the wild-type C57BL/6 isogenic parental strain. These results indicate that the heterozygous state in p53+/- mice, but not the v-Ha-ras transgene in Tg.AC mice can influence the induction of micronuclei by benzene.

Animals↗

Use of genetically modified mouse models for evaluation of carcinogenic risk: considerations for the laboratory animal scientist.

There has been increasing interest in the use of selected genetically modified (GM) mouse models for the testing of chemicals to determine their carcinogenic potential. GM mouse models are believed to be useful tools that offer mechanistically relevant insights for understanding and predicting the human response to chemical exposure. They have been proposed as alternatives to the traditional 2-year mouse oncogenicity bioassay. In this overview we will review the GM mouse models that have been proposed as bioassay alternatives and present some of the key laboratory animal science challenges that need to be considered when using these unique animals.

Animal Husbandry↗

Loss of p53 in benzene-induced thymic lymphomas in p53+/- mice: evidence of chromosomal recombination.

The purpose of this study was to examine the role of chromosomal recombination in mediating p53 loss in benzene-induced thymic lymphomas in C57BL/6-Trp53 haploinsufficient (N5) mice (p53+/- mice). We characterized loss of heterozygosity (LOH) on chromosome 11 using seven microsatellite markers in 27 benzene-induced and 6 spontaneous thymic lymphomas. Eleven patterns of LOH were found between the induced and spontaneous tumors, with only one pattern being in common between the tumor groups. Nearly 90% (24 of 27) of benzene-induced tumors exhibited loss of the functional p53 allele locus, and 83% (20 of 24) of these tumors retained two copies of the disrupted p53 allele. The results indicate that benzene induces a high frequency of LOH on chromosome 11 in p53+/- mice, likely mediated by aberrant chromosomal recombination.

Alleles↗

Inhibition of cytochrome P450 2E1 decreases, but does not eliminate, genotoxicity mediated by 1,3-butadiene.

1,3-Butadiene (BD), a rodent carcinogen, is metabolized to mutagenic and DNA-reactive epoxides. In vitro data suggest that this oxidation is mediated by cytochrome P450 2E1 (CYP2E1). In this study, we tested the hypothesis that oxidation of BD by CYP2E1 is required for genotoxicity to occur. Inhalation exposures were conducted with B6C3F1 mice using a closed-chamber technique, and the maximum rate of butadiene oxidation was estimated. The total amount of butadiene metabolized was then correlated with the frequency of micronuclei (MN). Three treatment groups were used: (1) mice with no pretreatment; (2) mice pretreated with 1,2-trans-dichloroethylene (DCE), a specific CYP2E1 inhibitor; and (3) mice pretreated with 1-aminobenzotriazole (ABT), an irreversible inhibitor of cytochromes P450. Mice in all 3 groups were exposed to an initial BD concentration of 1100 ppm, and the decline in concentration of BD in the inhalation chamber with time, due to uptake and metabolism of BD, was monitored using gas chromatography. A physiologically based pharmacokinetic model was used to analyze the gas uptake data, estimate V(max) for BD oxidation, and compute the total amount of BD metabolized. Model simulations of the gas uptake data predicted the maximum rate of BD oxidation would be reduced by 60% and 100% for the DCE- and ABT-pretreated groups, respectively. Bone marrow was harvested 24 h after the onset of the inhalation exposure and analyzed for frequency of micronuclei in polychromatic erythrocytes (MN-PCE). The frequency of MN-PCE per 1000 PCE in mice exposed to BD was 28.2 +/- 3.1, 19.8 +/- 2.5, and 12.3 +/- 1.9, for the mice with no pretreatment, DCE-pretreated mice and ABT-pretreated mice, respectively. Although inhibition of CYP2E1 decreased BD-mediated genotoxicity, it did not completely eliminate genotoxic effects. These data suggest that other P450 isoforms may contribute significantly to the metabolic activation of BD and resultant genotoxicity.

Administration, Inhalation↗

1,3-butadiene: cancer, mutations, and adducts. Part II: Roles of two metabolites of 1,3-butadiene in mediating its in vivo genotoxicity.

1,3-Butadiene (BD) is carcinogenic in mice and rats, with mice being more susceptible than rats to its carcinogenic effects. 1,3-Butadiene is mutagenic in the bone marrow and spleen cells of B6C3F1 lacI transgenic mice. The goal of this research was to assess the roles of two BD metabolites, 1,2-epoxy-3-butene (BDO) and 1,2,3,4-diepoxybutane (BDO2), in the mutagenicity and mutational spectrum of the parent compound BD by determining the mutagenicity and mutational spectra of BDO and BDO2 in human and rodent cells in vitro and in vivo. In human TK6 lymphoblastoid cells (TK6 cells), BDO exposure increased the frequency of G.C-->A.T transitions and A.T-->T.A transversions (Fisher exact test; p < 0.05). The most striking difference in the type of base-substitution mutations between BDO-exposed and BDO-unexposed TK6 cells was the 19-fold increase in A.T-->T.A transversions. 1,2,3,4-Diepoxybutane increased the frequency of A.T-->T.A transversions (Fisher exact test; p < 0.05) and the frequency of deletions in exposed TK6 cells compared with unexposed controls. Exposure of Rat2 lacI transgenic fibroblasts (Rat2 cells) to BDO increased the frequency of three types of base-substitution mutations: G.C-->A.T transitions, G.C-->T.A transversions, and A.T-->T.A transversions. Exposure of Rat2 cells to BDO2-induced dose-dependent increases in micronuclei at exposure levels that apparently did not induce mutagenicity at the lacI transgene. The lack of detectable mutagenicity at the lacI transgene in Rat2 cells exposed to BDO2 probably reflects the poor recovery of large deletions by this lambda phage-based mutagenicity assay. Inhalation exposure of B6C3F1 lacI transgenic mice (lacI mice) and F344 lacI transgenic rats (lacI rats) to BDO (29.9 parts per million [ppm]; 6 hours/day; 5 days/week for 2 weeks) did not increase the lacI mutant frequency (MF) in bone marrow or spleen cells of mice and rats, but in the cells of mouse lung (a tumor target organ for BD), significant mutagenicity was observed. An increased lacI MF was also observed in the bone marrow cells of rats exposed to BDO. Inhalation exposure of lacI mice and lacI rats to BDO2 (3.8 ppm; 6 hours/day; 5 days/week for 2 weeks) did not increase the lacI MF in bone marrow or spleen cells of mice or in the spleen cells of rats. An increased lacI MF was observed in the bone marrow cells of rats exposed to BDO2. In the present study, BDO specifically induced G.C-->A.T and A.T-->T.A transversions in vitro at both the endogenous hypoxanthine phosphoribosyltransferase (hprt) gene and the lacI transgene in Rat2 cells. It also induced an increased frequency of G.C-->T.A transversions in Rat2 cells. These types of mutations also occur at an increased frequency in mice exposed to the parent compound, BD. This finding demonstrates the induction of consistent mutational types across biological systems by BDO and indicates that BDO, but not BDO2, probably has a role in mediating the mutations recovered at the lacI transgene in animals exposed to the parent compound, BD. Therefore, it is apparent that in mice exposed to BD at carcinogenic levels, BDO and BDO2 act in concert to mediate the range of genotoxic responses. These data demonstrate that certain DNA adducts (guanine or adenine) may be useful biomarkers for BD genetic effects. However, other DNA lesions that can account for BDO2-induced deletions and chromosomal alterations also need to be considered as biomarkers for BD-induced genotoxicity.

Animals↗

Expression and distribution of cytochrome P450 2E1 in B6C3F1 mouse liver and testes.

Cytochrome P450 2E1 (CYP2E1) is believed to have a significant role in the bioactivation of 1,3-butadiene (BD) to DNA reactive epoxide metabolites that induce somatic and germ cell genotoxicity in mice. To assess the potential role of in situ bioactivation of BD by mouse testes for inducing germ cell genotoxicity, the presence of CYP2E1 in testes has been demonstrated by reverse transcriptase-polymerase chain reaction (RT-PCR), immunoprecipitation-Western blotting methods (IP-Western) and immunohistochemistry of tissue sections. Detection of CYP2E1 in the testes was limited to interstitial cells. In liver a known site of BD bioactivation and a positive control tissue used for these studies, a discrete, zonal staining pattern of liver CYP2E1 expression detected by immunohistochemical staining was shown. These results suggest that in situ bioactivation of BD in testes by CYP2E1 may contribute to BD-induced germ cell genotoxicity.

Animals↗

Persistence of N7-(2,3,4-trihydroxybutyl)guanine adducts in the livers of mice and rats exposed to 1,3-butadiene.

Liquid chromatography (LC) in combination with tandem mass spectrometry (MS/MS) and stable isotope methodology was employed for the analysis of the N7-guanine (Gua) adducts derived from 1,2:3, 4-diepoxybutane (BDO2) a reactive metabolite of 1,3-butadiene (BD). Two diastereomeric forms of N7-(2,3,4-trihydroxybutyl)guanine (THBG) were identified in the livers of both mice and rats. One of the diastereomers [(+/-)-THBG] was formed by reaction of DNA with (+/-)-BDO2, and the other diastereomer (meso-THBG) was formed by reaction of DNA with meso-BDO2. There was significantly more (+/-)-THBG and meso-THBG in the liver DNA of the mice when compared with those of the rats during the 10 days of exposure to BD and the 6 days of postexposure that were monitored. There was a 2-fold excess of (+/-)-THBG over meso-THBG in the rat liver at all the time points. In the mouse liver after 10 days of exposure to BD, the (+/-)-THBG (3.9 adducts/10(6) normal bases) was also present in an almost 2-fold excess over meso-THBG (2.2 adducts/10(6) normal bases). However, 6-days after exposure to BD, (+/-)-THBG (1.2 adducts/10(6) normal bases) and meso-THBG (1.0 adduct/10(6) normal bases) were present in almost equal amounts in the mouse liver. Furthermore, there was an almost 5-fold excess of the two THBG diastereomers in the mouse liver DNA 6 days after exposure to BD when compared with rat liver DNA. The half-lives of (+/-)-THBG and meso-THBG appeared to be slightly longer in mouse liver (4.1 and 5.5 days, respectively) than in rat liver (3.6 and 4.0 days, respectively). The apparent persistence of these adducts in the mouse may contribute to the increased susceptibility of this species to BD-induced carcinogenesis. It is possible that (+/-)-THBG and meso-THBG could have also been derived from the reaction of DNA with the hydrolysis product of BDO2, 1,2-dihydroxy-3,4-epoxybutane (DHEB). Surprisingly, a vast majority of the studies in which the mutagenic and carcinogenic potential of BDO2 have been examined have only employed the commercially available (+/-)-BDO2. In light of the present findings, additional studies will be required to determine the potency of meso-BDO2 and the DHEB that is the precursor to meso-THBG as mutagens and carcinogens.

Animals↗

Transgenic mouse mutation assay systems can play an important role in regulatory mutagenicity testing in vivo for the detection of site-of-contact mutagens.

Transgenic mouse mutation assays, such as MutaMouse (lacZ, CD2F1) and Big Blue (lacI, B6C3F1), afford the opportunity to evaluate the mutagenic potential of chemicals in any target organ in vivo. This paper discusses published data collected from the analysis of the skin, stomach and lung DNA after topical, oral and inhalation exposure, respectively. These data indicate that both MutaMouse and Big Blue should play an important part in the evaluation of genotoxicity in vivo, particularly where the endpoint or target tissue available in the more conventional tests is inappropriate. It is concluded that there is a distinct role for this type of assay in genetic toxicology testing. For substances applied to the skin or dosed orally or by inhalation and which are unlikely to reach either the bone marrow or the liver, then data derived from these assays may be more relevant to an assessment of possible risk to man than the currently used unscheduled DNA synthesis in liver and cytogenetics assays in bone marrow or peripheral blood.

Animals↗

The in vivo mutagenicity and mutational spectrum at the lacI transgene recovered from the spleens of B6C3F1 lacI transgenic mice following a 4-week inhalation exposure to 1,3-butadiene.

1,3-Butadiene (BD) is carcinogenic and mutagenic in B6C3F1 mice. We determined the lacI mutant frequency and mutational spectrum in spleen following inhalation exposure to BD at levels that are known to induce tumors. B6C3F1 lacI transgenic mice were exposed to air or to 62.5, 625, or 1250 ppm BD for 4 weeks (6 h/day, 5 days/week) and euthanized 14 days after the last exposure. BD increased the lacI mutant frequency in spleen at all levels of BD examined. In BD-exposed mice, an increased frequency of G:C-->A:T transitions occurred at non-5'-CpG-3' sites. Exposure to BD in B6C3F1 lacI transgenic mice also increased the frequency of base substitution mutations that occurred at A:T base pairs when compared to air controls. The increased frequency of specific mutations at G:C base pairs in spleen was not observed in our previous studies in bone marrow and indicates tissue-specific differences in the BD-induced mutational spectrum. These data demonstrate that in vivo transgenic mouse mutagenicity assays can identify tissue-specific mutagenicity and mutational spectrum responses of genotoxic carcinogens at exposure levels that are known to induce tumors.

Administration, Inhalation↗

Genetic instability in human T-lymphocytes.

Mutations arising in vivo in the hypoxanthine-guanine phosphoribosyltransferase (HPRT) gene of T-lymphocytes provide a measure of mutation induction in human somatic cells. Studies of measured background HPRT mutant frequency (MF) values show wide inter-individual variation. At the extremes are individuals with 'outlier' MF values, i.e., non-exposed individuals with MF>100x10-6 [Robinson et al., Mutation Res. 313 (1994) 227-247.]. The elevated HPRT MF in one well-studied outlier is due to the in vivo expansion of mutant cells possessing an identical T-cell receptor (TCR) gene rearrangement pattern. We report here that this in vivo expanding TCR clone shows multiple different HPRT mutations and thus possesses a mutator phenotype. Other individuals with T-cell mutator phenotypes have been found, suggesting that this phenomenon may contribute to the extremes of variation in HPRT MFs in the human population.

Adult↗

Long-term mutagenicity studies with chloroform and dimethylnitrosamine in female lacI transgenic B6C3F1 mice.

The weight of evidence indicates that chloroform induces cancer in the female B6C3F1 mouse liver via a nongenotoxic-cytotoxic mode of action. However, it is probable that DNA damage occurs secondary to events associated with cytolethality and regenerative cell proliferation. The purpose of the present study was to evaluate the potential mutagenic activity of chloroform in the B6C3F1 lacI transgenic mouse liver mutagenesis assay including mutagenic events that might occur secondary to cytolethality. The positive control, dimethylnitrosamine (DMN) is a DNA-reactive mutagen and carcinogen. DMN-induced mutations were anticipated to require only a brief exposure and without further treatment were predicted to remain unchanged over time at those frequencies. Chloroform-induced mutations secondary to toxicity were anticipated to require longer exposure periods and to occur only under conditions that produced sustained cytolethality and regenerative cell proliferation. Female B6C3F1 lacI transgenic mice were treated with daily doses of 2, 4, or 8 mg/kg of DMN by gavage for 4 days and then held until analysis 10, 30, 90, and 180 days postexposure. Livers from DMN-treated mice exhibited a dose-related 2- to 5-fold increase over control mutant frequencies and remained at those levels for 10 through 180 days postexposure. Thus, following the initial induction by DMN no selective mutation amplification or loss was seen for this extended period of time. Female B6C3F1 lacI mice were exposed daily for 6 hr/day 7 days/week to 0, 10, 30, or 90 ppm chloroform by inhalation, representing nonhepatotoxic, borderline, or overtly hepatotoxic chloroform exposures. Timepoints for determination of lacI mutant frequency were 10, 30, 90, and 180 days of exposure. No increase in lacI mutant frequency in the liver was observed at any dose or timepoint with chloroform, indicating a lack of DNA reactivity. DNA alterations secondary to toxicity either did not occur or were of a type not detectable by lacI mutant frequency analysis, such as large deletions.

Administration, Inhalation↗

Molecular analysis of lacI mutants from transgenic fibroblasts exposed to 1,2-epoxybutene.

1,3-Butadiene (BD) is a genotoxic carcinogen that is bioactivated to at least two mutagenic metabolites: 1,2-epoxybutene (EB) and 1,2:3,4-diepoxybutane (DEB). We reported previously that lacI transgenic mice exposed to BD had an increased frequency of specific base substitution mutations in the bone marrow and spleen relative to unexposed controls. In the experiments described here, we determined the mutagenicity and mutational spectrum of EB in Rat2 lacI transgenic fibroblasts as a means of assessing the contribution of this metabolite to the lacI mutational spectrum of BD. Rat2 cells were exposed to 0, 0.4, 0.6, 0.8 or 1.0 mM EB for 24 h, resulting in a range of cell survival from 100 to 15%, respectively. Mutagenicity was assessed at 0, 0.6 and 1.0 mM EB. Unexposed controls had a background mutant frequency of 6 +/- 1 +/- 10(-5), while the mutant frequency in cells exposed to 0.6 and 1.0 mM EB was increased 2- and 3-fold, respectively. DNA sequence analysis of 154 lacI mutants recovered in these experiments revealed an increase in the frequency of specific base substitution mutations in cells exposed to 1.0 mM EB compared with controls. These included G:C-->A:T transitions at non-CpG sites, G:C-->T:A transversions and A:T-->T:A transversions, which have all been observed in lacI mutants isolated from transgenic mice exposed to BD. These results suggest that EB causes mutation primarily by base substitution and that the spectrum of these mutations closely resembles that of BD. These data, along with previous findings from our laboratory, suggest that EB is more likely than DEB to be primarily responsible for the lacI mutational spectrum observed in lacI transgenic mice exposed to BD.

Animals↗

Comparison of the mutagenic potency of 1,3-butadiene at the hprt locus of T-lymphocytes following inhalation exposure of female B6C3F1 mice and F344 rats.

1,3-Butadiene (BD) is an indirect alkylating agent that has greater cancer potency in the mouse than in the rat. The purpose of the present study was to compare the mutagenic potency of BD at the hprt locus of T-lymphocytes of exposed mice and rats and to determine whether mutations induced in this marker gene can be used as a quantitative indicator for species differences in susceptibility to cancer. To this end, experiments were conducted to define the effects of exposure duration and the time elapsed after exposures on the frequency of hprt mutations (Mf) in T-cells from female B6C3F1 mice and F344 rats of similar age (4-5 weeks) when exposed to BD by inhalation. The accumulation of hprt mutations in T-cells from thymus was assessed in animals necropsied 2 weeks after exposure to 0 or 1250 ppm BD for 1 or 2 weeks, while the time course for the appearance of hprt mutant T-cells (i.e., the phenotypic expression and cell migration) in thymus and spleen was evaluated in animals necropsied at weekly/biweekly intervals up to 10 weeks after exposure for 2 weeks. At necropsy, T-cells were isolated from thymus and spleen and cultured in the presence of IL-2, concanavalin A, and 6-thioguanine (Walker and Skopek, Mutat. Res., 288, 151-162, 1993). BD exposures of 1 and 2 weeks led to mutagenic effects in mouse thymus, with the average Mfs being 3- and 5-fold greater than background values, respectively. In rat thymus, there was only a 1.7-fold increase in Mfs after 2 weeks of BD exposure. In the mutant expression experiment, hprt Mfs in thymus and spleen of both species increased for several weeks post-exposure and then declined. Hprt Mfs in thymus reached maximum levels at 2 weeks post-exposure in mice (Mfs = 11.3 +/- 2.4 x 10(-6)) and at 3 weeks post-exposure in rats (4.9 +/- 1.2 x 10(-6)), while hprt Mfs in spleen reached peak levels at 5 weeks post-exposure in mice (19.7 +/- 1.9 x 10(-6)) and 4 weeks post-exposure in rats (10.1 +/- 1.8 x 10(-6)). Background Mfs for mouse and rat thymus and spleen ranged from 1.6 +/- 0.3 x 10(-6) to 3.0 +/- 1.1 x 10(-6). Statistical analyses of the hprt Mf data for spleen demonstrated that, under these exposure conditions, the mutagenic potency of BD (represented by the difference in the areas under the phenotypic expression curves of treated versus control animals) was 5-fold greater in mice than in rats. The magnitude of the species differences in mutagenic potency, observed after 2 weeks of BD exposure, resembles the species differences in metabolism more closely than the species differences in cancer potency.

Animals↗