In vivo repair of DNA damage induced by X-rays in the early stages of mouse fertilization, and the influence of maternal PARP1 ablation.

The early pronucleus stage of the mouse zygote has been characterised in vitro as radiosensitive, due to a high rate of induction of chromosome-type chromosome abnormalities (CA). We have investigated the repair of irradiation induced double strand DNA breaks in vivo by γH2AX foci and first cleavage metaphase analysis. Breaks were induced in sperm and in the early zygote stages comprising sperm chromatin remodelling and early pronucleus expansion. Moreover, the role of PARP1 in the formation and repair of spontaneous and radiation-induced double strand breaks in the zygote was evaluated by comparing observations in C57BL/6J and PARP1 genetically ablated females. The results confirmed in vivo that the rate of chromosome aberration induction by X-rays was approximately 3-fold higher in the zygote than in mouse lymphocytes. This finding was related to a diminished efficiency of double strand break signalling, as shown by a lower rate of γH2AX radiation-induced foci compared to that measured in most other somatic cell types. The spontaneous frequency of CA in PARP1 depleted zygotes was slightly but significantly higher than in wild type zygotes. Also, these zygotes showed some impairment of the radiation-induced DNA Damage Response when exposed closer to the start of S-phase, revealed by a higher number of γH2AX foci and a longer cell cycle delay. The rate of chromosome aberrations, however, was not elevated over that of wild type zygotes, possibly thanks to backup repair pathways and/or selection mechanisms against damaged cells. When comparing with the literature data on irradiation induced CA in mouse zygotes in vitro, the levels of induction were strikingly similar as was the frequency of misrepair of double strand breaks (γH2AX foci). This result can be reassuring for in vitro human gamete and embryo handling, because it shows that culture conditions do not significantly affect double strand DNA break repair.

Environmental hazard in the aetiology of somatic and germ cell aneuploidy.

Sources of environmental exposures to potentially aneugenic agents are many and include occupational and therapeutic exposures, and exposures associated with lifestyle habits. In this present study, some of these agents and exposure scenarios are discussed that involve potentially large population targets and/or seem to affect chromosome segregation by previously unsuspected mechanisms: metals, possibly acting by epigenetic mechanisms; nano-sized particles that might directly interact with subcellular components of the mitotic and meiotic machineries; cytostatic drugs in healthcare occupations; anticancer therapies potentially affecting the genetic integrity of gametes; continuously increasing electromagnetic field exposures with some sparse evidence of aneugenic activity; endocrine disruptors and their seemingly elusive effects in mouse oocytes, including the first evidence that prenatal exposure could affect meiotic nondisjunction in adult life. Hazards are considered for both somatic cells at risk of neoplastic transformation or tumour progression by chromosome loss and gain and germ cells at risk of heritable aneuploidies associated with spontaneous abortions or genetic diseases. Finally, possible synergistic interactions between environmental exposure and ageing or genetic predisposition are considered that could influence ultimate risks.

Evaluation of aneugenic effects of bisphenol A in somatic and germ cells of the mouse.

Bisphenol A (BPA) is a synthetic monomer widely used to polymerize polycarbonate plastics and resins. It is shown in vitro to interfere with microtubules, producing aberations in mitotic and meiotic spindles. An increase of meiotic abnormalities in untreated female mice from an experimental colony was temporally correlated with the accidental release of BPA from polycarbonate cages and bottles damaged by inadvertent treatment with harsh alkaline detergents [P.A. Hunt, K.E. Koehler, M. Susiarjo, C.A. Hodges, A. Ilagan, R.C. Voigt, S. Thomas, B.F. Thomas, T.J. Hassold, Bisphenol A exposure causes meiotic aneuploidy in the female mouse, Curr. Biol. 13 (2003) 546-553]. In the present study, potential aneugenic effects of BPA on mouse male and female germ cells and bone marrow cells have been evaluated after acute, sub-chronic or chronic in vivo exposure. Female mice were orally treated with a single BPA dose, with 7 daily administrations or exposed for 7 weeks to BPA in drinking water. No significant induction of hyperploidy or polyploidy was observed in oocytes and zygotes at any treatment condition. The only detectable effect was a significant increase of metaphase II oocytes with prematurely separated chromatids after chronic exposure; this effect, however, had no irreversible consequence upon the fidelity of chromosome segregation during the second meiotic division, as demonstrated by the normal chromosome constitution of zygotes under the same exposure condition. With male mice, no delay of meiotic divisions was found after six daily oral doses of BPA with the BrdU assay. Similarly, no induction of hyperploidy and polyploidy was shown in epydidimal sperm hybrized with probes for chromosomes 8, X and Y, 22 days after six daily oral BPA doses. Finally, two daily oral BPA doses did not induce any increase of micronucleus frequencies in polychromatic erythrocytes of mouse bone marrow. In conclusion, our results do not add evidence to the suspected aneugenic activity of BPA and suggest that other factors or co-factors should be considered to explain the unexpected burst of meiotic abnormalities previously attributed to accidental BPA exposure.

Gender effects on the incidence of aneuploidy in mammalian germ cells.

Aneuploidy occurs in 0.3% of newborns, 4% of stillbirths, and more than 35% of all human spontaneous abortions. Human gametogenesis is uniquely and gender-specific susceptible to errors in chromosome segregation. Overall, between 1% and 4% of sperm and as many as 20% of human oocytes have been estimated by molecular cytogenetic analysis to be aneuploid. Maternal age remains the paramount aetiological factor associated with human aneuploidy. The majority of extra chromosomes in trisomic offspring appears to be of maternal origin resulting from nondisjunction of homologous chromosomes during the first meiotic division. Differences in the recombination patterns between male and female meiosis may partly account for the striking gender- and chromosome-specific differences in the genesis of human aneuploidy, especially in aged oocytes. Nondisjunction of entire chromosomes during meiosis I as well as premature separation of sister chromatids or homologues prior to meiotic anaphase can contribute to aneuploidy. During meiosis, checkpoints at meiotic prophase and the spindle checkpoint at M-phase can induce meiotic arrest and/or cell death in case of disturbances in pairing/recombination or spindle attachment of chromosomes. It has been suggested that gender differences in aneuploidy may result from more permissive checkpoints in females than males. Furthermore, age-related loss of chromosome cohesion in oocytes as a cause of aneuploidy may be female-specific. Comparative data about the susceptibility of human male and female germ cells to aneuploidy-causing chemicals is lacking. Increases of aneuploidy frequency in sperm have been shown after exposure to therapeutic drugs, occupational agents and lifestyle factors. Conversely, data on oocyte aneuploidy caused by exogenous agents is limited because of the small numbers of oocytes available for analysis combined with potential maternal age effects. The vast majority of animal studies on aneuploidy induction in germ cells represent cause and effect data. Specific studies designed to evaluate possible gender differences in induction of germ cell aneuploidy have not been found. However, the comparison of rodent data available from different laboratories suggests that oocytes are more sensitive than male germ cells when exposed to chemicals that effect the meiotic spindle. Only recently, in vitro experiments, analyses of transgenic animals and knockdown of expression of meiotic genes have started to address the molecular mechanisms underlying chromosome missegregation in mammalian germ cells whereby striking differences between genders could be shown. Such information is needed to clarify the extent and the mechanisms of gender effects, including possible differential susceptibility to environmental agents.

Effect of p53 haploinsufficiency on melphalan-induced genotoxic effects in mouse bone marrow and peripheral blood.

Mice heterozygous for a p53 null mutation develop tumours induced by genotoxic carcinogens with a shorter latency than wild type mice and have been proposed as an alternate animal model for carcinogenicity testing. Some literature data suggest that p53+/- mice might also be more sensitive to the short-term effects of genotoxic agents and manifest a haploinsufficiency phenotype that could contribute to the higher tumour susceptibility. We have compared the induction of micronuclei in bone marrow and blood of p53+/- and p53+/+ isogenic mice after treatment with a single or multiple doses of melphalan (MLP), a crosslinking genotoxic carcinogen. We have also characterized the mechanism of micronucleus induction with CREST staining of kinetochore proteins to distinguish between chromosome break- and chromosome loss-induced micronuclei. Significant increases of micronucleated bone marrow polychromatic erythrocytes and blood reticulocytes were induced under all MLP exposure conditions. The frequency of micronucleated blood erythrocytes increased linearly with duration of exposure. Micronuclei were essentially a consequence of chromosome break events. After a single MLP dose, a significant reduction of the frequency of polychromatic erythrocytes in bone marrow of p53+/+ animals suggested the induction of cytotoxicity/cell cycle delay. This effect was not observed in p53+/- mice. We believe this finding to provide some evidence of a haploinsufficiency phenotype in the modulation of cell cycle/apoptotic pathways mediated by the p53 protein. In bone marrow of wild type mice, an increased effect of multiple MLP doses was detected over that of a single administration, whereas, in p53+/- mice, no differential effect was found of different exposure durations. Possibly, the probability of micronucleus formation increased under chronic exposure because of increased cell division in response to peripheral anemia and a reduction of p53 protein level had a small effect on cell cycle modulation and on such indirect mechanism of micronucleus induction. However, pairwise comparisons between the frequencies of cells with micronuclei in wild type and p53+/- mice under all exposure conditions did not show statistically significant differences, suggesting that the observed effects of p53 haploinsufficiency were weak and temporary and a higher/faster induction of irreversible chromosome damage could not account for the increased susceptibility of p53+/- mice to MLP-induced tumours.

Nondisjunction rates of mouse chromosomes involved in heterozygous Rb rearrangements measured by chromosome painting of spermatocytes. II. The effects of trivalent combinations and genetic background.

Chromosome specific nondisjunction rates were quantified by dual-colour FISH in spermatocytes II of Robertsonian heterozygous mice with different trivalent combinations or, alternatively, with different genetic backgrounds. We found that such factors do not influence the proneness to nondisjunction of specific chromosomes.

Nondisjunction rates of mouse specific chromosomes involved in heterozygous Rb rearrangements measured by chromosome painting of spermatocytes II. I. The effects of the number of trivalents.

Dual-colour FISH painting with alternative fluorescent chromosome-specific probes allowed us to distinguish chromosomes 1, 4, 6 and 14. The purpose was to check whether nondisjunction rates of specific chromosomes involved in heterozygous Robertsonian fusions are independent of the number of trivalents, or an epistatic effect among Rb chromosomes takes place affecting nondisjunction rates. Probes were used on DAPI-stained metaphases of spermatocytes II of laboratory strains of mice with reconstructed karyotypes heterozygous for one, two, three or four Robertsonian metacentrics in an all-acrocentric background. The existence of such epistatic interactions was not verified.

Cosegregation of Robertsonian metacentric chromosomes in the first meiotic division of multiple heterozygous male mice as revealed by FISH analysis of spermatocyte II metaphases.

Contrasting results (random segregation or cosegregation of isomorphic chromosomes) have been reported up to now on the segregation pattern of Robertsonian metacentric chromosomes of Mus musculus domesticus in multiple heterozygotes, using different approaches (karyotypical analysis of the progeny or of second meiotic metaphases). In the present contribution data are presented based on FISH (Fluorescence In Situ Hybridisation) analysis with telomeric probes, which allowed us to distinguish metacentric chromosomes from pairs of acrocentric chromosomes with their centromeric regions close to each other. Probes were hybridized to DAPI stained metaphases of spermatocytes II of mice heterozygous for two, three or four Robertsonian metacentrics in an all-acrocentric background, the karyotype of which has been reconstructed starting from laboratory strains. Isomorphic chromosomes tend to cosegregate (metacentrics with metacentrics, acrocentrics with acrocentrics); the values found for cosegregation have a clear even if moderate effect on the reproductive isolation caused by underdominant chromosomal rearrangements.

Cytogenetic biomonitoring of workers from laboratories of clinical analyses occupationally exposed to chemicals.

A cytogenetic monitoring study was carried out on a group of workers in clinical analysis laboratories to investigate the risk of occupational exposure to chronic low levels of chemicals.Thirty-four clinical laboratories have been involved in the study. In these laboratories, toxicants and analytical procedures utilized have been characterized. The individual occupational exposure of workers was assessed by use of a questionnaire concerning the chemical substances utilized. About 300 different chemicals have been identified. Cytogenetic analyses (chromosomal aberration and micronucleus tests) were carried out on a strictly selected group of 50 workers enrolled from these laboratories and compared to 53 controls (healthy blood donors) matched for gender and age. The exposed group shows a significantly higher frequency of genetic damage than the control group. Both chromatid and chromosome aberration frequencies in workers appear significantly higher than in controls. Similarly, comparison between micronucleated cells rates of exposed and unexposed groups show significantly higher frequencies of binucleated cells with micronucleus (BNMN) and of total micronuclei (MN tot) in workers than in controls.

Genotoxic effects of butadiene in mouse lung cells detected by an ex vivo micronucleus test.

Lung fibroblasts from BD-exposed mice have been analysed for the occurrence of micronuclei. Primary cultures set up 24h after the end of exposure were treated with cytochalasin B and micronuclei scored in binucleate cells. A three-fold statistically significant increase of micronucleated cells was detected after exposure to 500ppm, the lowest tested concentration. A linear dose effect relationship was observed between 500 and 1300ppm. Immunofluorescent staining of kinetochore proteins was applied to distinguish between acentric micronuclei produced by chromosome breaks and micronuclei containing a centromeric region, most likely induced by chromosome loss. A statistically significant increase of both types of MN in 1300ppm-exposed females and a significant increase in centromeric MN in 500ppm-exposed males were detected. These data demonstrate that an intermediate of BD metabolism with a potential for clastogenic and aneugenic effects is active in lung cells after inhalation exposure. These effects can play a role in the initiation and promotion of BD-induced lung tumours.

Butadiene diolepoxide- and diepoxybutane-derived DNA adducts at N7-guanine: a high occurrence of diolepoxide-derived adducts in mouse lung after 1,3-butadiene exposure.

Butadiene (BD) is a high production volume chemical and is known to be tumorigenic in rodents. BD is metabolized to butadiene monoepoxide (BMO), diepoxybutane (DEB) and butadiene diolepoxide (BDE). These epoxides are genotoxic and alkylate DNA both in vitro and in vivo, mainly at the N7 position of guanine. In this study, a 32P-post-labeling/thin-layer chromatography (TLC)/high-pressure liquid chromatography (HPLC) assay for BDE and DEB adducts at the N7 of guanine was developed and was used in determining the enantiomeric composition of the adducts and the organ dose of BD exposure in lung. Exposure of 2'-deoxyguanosine (dGuo), 2'-deoxyguanosine-5'-phosphate (5'-dGMP) and 2'-deoxyguanosine-3'-phosphate (3'-dGMP) to racemic BDE followed by neutral thermal hydrolysis gave two products (products 1 and 2) that were identified by MS and UV and NMR spectroscopy as a diastereomeric pair of N7-(2,3,4-trihydroxybutan-1-yl)-guanines. Exposure of dGuo nucleotides to RR/SS DEB (also referred to as dl DEB) followed by thermal depurination resulted in a single product coeluting with the BDE product 1. If the reaction mixture of BDE and 5'-dGMP was analyzed by HPLC before hydrolysis of the glycosidic bond, four major nucleotide alkylation products (A, B, C and D) with identical UV sepectra were detected. The products were isolated and hydrolyzed, after which A and C coeluted with product 1 and B and D coeluted with the product 2. The major adduct of DEB-exposed 5'-dGMP was N7-(2-hydroxy-3,4-epoxy-1-yl)-dGMP (product E). A 32P-post-labeling assay was used to detect BDE- and DEB-derived N7-dGMP adducts in DNA. Levels of adducts increased with a dose of BDE and DEB and exhibited a half life of 30 +/- 3 (r = 0.98) and 31 +/- 4 h (r = 0.95), respectively. Incubation of DEB-modified DNA at 37 degrees C at neutral pH for up to 142 h did not lead to an increase of N7-(2,3,4-trihydroxybutan-1-yl)-dGMP in the DNA. These observations led to the conclusion that the N7-(2,3, 4-trihydroxybutan-1-yl)-dGMP adducts in DNA can be used as a marker of BDE exposure and that N7-(2-hydroxy-3,4-epoxy-1-yl)-dGMP adducts are related to DEB exposure. Dose-related levels of BDE- and DEB-derived adducts were detected in lungs of mice inhaling butadiene. Most of the N7-dGMP adducts (73%; product D) were derived from the 2R-diol-3S-epoxide of 1,3-butadiene. The data presented in this paper indicate that in vivo, 98% of N7-dGMP alkylation after BD exposure is derived from BDE, and approximately 2% of the adducts were derived from DEB and BMO.

Measurement and characterization of micronuclei in cultured primary lung cells of mice following inhalation exposure to benzene.

The genotoxic effects of benzene in lung cells of mice exposed to single acute doses by inhalation have been estimated by cytogenetic analysis of micronuclei in primary cultures of lung fibroblasts. Mice were nose-only exposed to 1000 p.p.m. for 30 or 60 min or to 3500 p.p.m. for 30 min and sacrificed 24 h after the end of exposure. Lung fibroblasts were cultured attached to coverslips for 72 h, the last 48 h in the presence of 0.75 microgram/ml cytochalasin B. Micronuclei were scored in binucleate cells. The mechanism(s) of micronucleus induction was characterized by immunofluorescent staining of kinetochore proteins (CREST staining), which allowed micronuclei due to chromosome loss (kinetochore-positive) to be distinguished from those produced by chromosome breakage (kinetochore-negative). Three- and 4-fold statistically significant increases in total micronucleus frequencies were observed in all benzene-exposed mice with respect to unexposed controls. The effect was neither concentration nor time dependent. This is compatible with a plateau dose-effect relationship for the effects on bone marrow, which is explained by saturation of metabolism. Both chromosome loss and chromosome breakage appear to contribute to micronucleus formation, suggesting that in addition to chromosome rearrangements, aneuploidy may be a relevant early genotoxic event associated with benzene carcinogenicity. Under the same treatment conditions no micronucleus induction could be shown in spleen lymphocytes, suggesting that with very short benzene exposures cells at the first contact site with local metabolizing capacity have a higher probability of genetic alterations potentially leading to neoplasia.

Analysis of micronuclei and DNA single-strand breaks in mouse splenocytes and peripheral lymphocytes after oral administration of tetramethylthiuram disulfide (thiram).

The fungicide thiram (tetramethylthiuram disulfide, TMTD) was administered by repeated oral intubations to groups of male B6C3F1 mice at 100, 300 and 900 mg/kg body weight for 4 consecutive days, or at 300 mg/kg for 8 and 12 days. 24 hr after the last treatment animals were killed, and splenocyte cultures were set up for the analysis of micronuclei by the cytokinesis-block method. DNA single strand breaks (ssb) and alkali labile sites were also analysed by the single cell gel electrophoresis (Comet) assay in splenocytes and lymphocytes of animals receiving the 8- and 12-day treatments. Parallel experiments with human peripheral lymphocytes were carried out to assess the ability of thiram to induce micronuclei and DNA ssb and alkaline labile sites under in vitro conditions. No significant increase of micronucleated splenocytes was observed in treated animals, despite some evidence of treatment-related cellular toxicity. A borderline excess of DNA damage was suggested by the Comet assay on circulating lymphocytes, whereas negative results were obtained with splenocytes. In vitro, positive results with both genetic end points were obtained in assays with human lymphocytes in the dose ranges 0.5-24 microg/ml and 0.1-8 microg/ml for micronucleus and Comet assays, respectively. These results suggest that thiram, despite its established genotoxicity in vitro, is devoid of appreciable clastogenic and/or aneugenic activity in vivo after oral administration to mice at the maximum tolerated dose.

DNA adducts in mouse testis and lung after inhalation exposure to 1,3-butadiene.

1,3-Butadiene is a widely used industrial chemical and also an environmental contaminant. Recent findings have shown that butadiene can also be a male germ cell mutagen. In this study, DNA adduct formation in testis and lung has been explored by using N7-alkylated guanines as a marker of biological effective dose. The adducts measured were the four structurally different guanine N7-adducts alkylated by butadienemonoepoxide, the main metabolite of 1,3-butadiene. This study demonstrates the dose-dependent adduct formation in lung and testis. At lower exposures (50 and 200 ppm) the adduct levels were about the same in the two organs, but at 500 ppm the adduct level was significantly (p < 0.03) higher in testis than in lung. The enantiomeric composition of the adducts detected was also different. In lung, all 4 possible adducts were present (S-C-1" dominating, 49%), but in testis only two out of four adducts were detected (S-C-2" being the most abundant adduct, 71%). These novel observations indicate that the DNA repair is different in these two organs studied and that heritable genetic effects observed may be mediated through the DNA adducts.

Diepoxybutane cytotoxicity on mouse germ cells is enhanced by in vivo glutathione depletion: a flow cytometric approach.

Diepoxybutane is one of the key metabolites of butadiene, a compound of high environmental and occupational concern. The effects of diepoxybutane on mouse reproductive cells have been previously characterized by flow cytometry demonstrating a specific, dose-dependent cytotoxicity for differentiating spermatogonia. It is known that butadiene epoxides, deriving from butadiene bioactivation by cytochrome P450-monooxygenase systems, can be enzymatically conjugated to glutathione by glutathione S-transferases. In this paper, we tested the hypothesis whether a pretreatment with phorone, a well-known intracellular glutathione depleter, would enhance the germ cell cytotoxicity of diepoxybutane. Results were consistent with an active role played in vivo by the glutathione-detoxifying system, as diepoxybutane cytotoxicity was increased after chemically induced reduction of glutathione concentration.

Reproductive toxicity of 1,3-butadiene in the mouse: cytogenetic analysis of chromosome aberrations in first-cleavage embryos and flow cytometric evaluation of spermatogonial cell killing.

Reproductive effects of 1,3 butadiene inhalation have been evaluated in male mice by reduction of post-meiotic germ cells, alteration of sperm chromatin structure and transmission of chromosome aberrations to one-cell embryos. Animals were exposed for 5 consecutive days for 6 h per day to butadiene concentrations of 130, 500 or 1300 ppm. The testicular fraction of post-meiotic germ cells was measured by flow cytometric analysis on the basis of their DNA content. Round spermatids were discriminated from mature, elongated spermatids by their different degree of chromatin condensation. Butadiene-induced cytotoxic effects on differentiating spermatogonia were shown by a concentration-dependent decrease of round spermatids occurring 21 days after chemical exposure, confirmed by a similar decrease of elongated spermatids measured in testes sampled 7 days later. Statistically significant effects were seen already at 130 ppm. An incomplete repopulation of the elongated spermatid compartment observed 35 days after exposure to 1300 ppm suggested that, at the highest concentration tested, butadiene toxicity extended to stem cells. Alterations of sperm chromatin were revealed by its increased sensitivity to acidic denaturation in situ. The percentage of abnormal sperm was significantly increased after butadiene exposure of differentiating spermatogonia and spermatocytes. This suggested the induction of persistent effects interfering with chromatin remodelling during spermiogenesis. Chromosome-type structural aberrations were significantly elevated in first-cleavage embryos conceived by males mated during the first and second week after the end of exposure. The lowest effective tested concentration was 500 ppm, the same reported for dominant lethal induction under identical exposure conditions. As in the dominant lethal assay, the effect of this dose was confined to exposed sperm, while both sperm and late spermatids were affected by the inhalation of 1300 ppm. A quantitative comparison between the effects induced by intraperitoneal injections of diepoxybutane or butadiene inhalations suggested that other reactive intermediates, in addition to diepoxybutane, might contribute to mediate butadiene-induced reproductive toxicity.

Genetic effects of 1,3-butadiene and associated risk for heritable damage.

A summary of the results of the studies conducted in the EU Project "Multi-endpoint analysis of genetic damage induced by 1,3-butadiene and its major metabolites in somatic and germ cells of mice, rats and man" is presented. Results of the project are summarized on the detection of DNA and hemoglobin adducts, on the cytotoxic and clastogenic effects in somatic and germinal cells of mice and rats, on the induction of somatic mutations at the hprt locus of experimental rodents and occupationally exposed workers, on the induction of dominant lethal mutations in mice and rats, and on heritable translocations induced in mice, after exposure to butadiene (BD) or its major metabolites, butadiene monoepoxide (BMO), diepoxybutane (DEB) and butadiene diolepoxide (BDE). The primary goal of this project was to collect experimental data on the genetic effects of BD in order to estimate the germ cell genetic risk to humans of exposure to BD. To achieve this, the butadiene exposure are based on data for heritable translocations and bone marrow micronuclei induced in mice and chromosome aberrations observed in lymphocytes of exposed workers. A doubling dose for heritable translocations in human germ cells of 4900 ppm/h is estimated, which, assuming cumulative BD exposure over the sensitive period of spermatogenesis, corresponds to 5-6 weeks of continuous exposure at the workplace to 20-25 ppm. Alternatively, the rate of heritable translocation induction per ppm/h of BD exposure is estimated to be approximately 0.8 per million live born, compared to a spontaneous incidence of balanced translocations in humans of approximately 800 per million live born. These estimates have large confidence intervals and are only intended to indicate orders of magnitude of human genetic risk. These risk estimates are based on data from germ cells of BD-exposed male mice. The demonstration that clastogenic damage was induced by DEB in preovulatory oocytes at doses which were not ovotoxic implies that additional studies on the response of mammalian female germ cells to BD and its metabolites are needed. The basic assumption of the above genetic risk estimates is that experimental mouse data obtained after BD exposure can be extrapolated to humans. Several points exist in the present report and in the literature which contradict this assumption: (1) the level of BMO-hemoglobin adducts was significantly elevated in BD-exposed workers; however, it was considerably lower than would have been predicted from comparable rat and mouse exposures; (2) the concentrations of the metabolites DEB and BMO were significantly higher in mouse than in rat blood after BD exposure. Thus, while metabolism of BD is qualitatively similar in the two species, it is quantitatively different; (3) no increase of HPRT mutations was shown in 19 workers exposed on average to 1.8 ppm of BD, while in a different population of workers from a US plant exposed on average to 3.5 ppm of BD, a significant increase of HPRT variants was detected; and (4) data from cancer bioassays and cancer epidemiology suggest that rat is a more appropriate model than mouse for human cancer risk from BD exposure. However, the dominant lethal study in rats gave a negative result. At present, we do not know which BD metabolite(s) may be responsible for the genetic effects even though the bifunctional alkylating agent DEB is the most likely candidate for the induction of clastogenic events. Unfortunately, methods to measure DEB adducts in hemoglobin or DNA are only presently being developed. Despite these several uncertainties the use of the mouse genetic data is regarded as a justifiable and conservative approach to human genetic risk estimation given the considerable heterogeneity observed in the biotransformation of BD in humans.

32P-postlabelling/HPLC assay reveals an enantioselective adduct formation in N7 guanine residues in vivo after 1,3-butadiene inhalation exposure.

We have established a protocol that allows qualitative and quantitative determination of butadiene monoepoxide-DNA adducts formed as a result of inhalation exposure to 1,3-butadiene. We observed that in this particular case in vivo samples required extensive sample purification to facilitate a low background. Sample preparation included a solid phase extraction carried out with a strong anion exchange column and one-dimensional ion exchange TLC. The ultimate analysis is based on reverse phase HPLC with on-line radioactivity and UV detectors. The qualitative identification and quantitation is based on characterized markers, which are used as external and internal standards. Modified 3'-dGMP markers were used to control labelling efficiency, which varies, and modified 5'-dGMP markers were used as an optical standard to qualitatively assign the products and to determine recovery of the sample preparation. Using this method we were able to demonstrate, for the first time, specific enantio- and regioisomeric adduct formation at the N7 position of guanine residues in liver DNA of rats inhalation-exposed to 1,3-butadiene. The major adduct formed was the C-2 isomer derived from the R enantiomer of butadiene monoepoxide, contributing 47% of all adducts formed at the N7 position of guanine. The relative proportions of the remaining three other adducts detected were 22 (R C-1), 18 (S C-2) and 14% (S C-1) respectively. Inhalation exposure to 200 p.p.m. for 5 days resulted in an alkylation level of 7.2 fmol/10 microg DNA or 2.4 adducts/10(-7) normal nucleotides.

Induction and transmission of chromosome aberrations in mouse oocytes after treatment with butadiene diepoxide.

A study was conducted on the genotoxicity of butadiene diepoxide (DEB) in mouse oocytes. Superovulated female mice were injected intraperitoneally with DEB and mated with untreated males. Oocyte exposure occurred approximately 1.5 days before ovulation. DEB doses ranged between 26 and 52 mg/kg. Chromosome aberrations were scored in C-banded metaphases of one-cell embryos. The percentage of mated females, the average number of zygotes harvested per female, the frequencies of unfertilized oocytes and developmentally delayed zygotes did not reveal any overt sign of chemical toxicity which hindered the propensity of animals to mate or affected the ovulation, fertilization, or cell cycle progression of treated oocytes. A dose-dependent induction of chromosome aberrations was observed which was best fitted by a linear-quadratic equation. Half of all the aberrations transmitted by DEB-treated oocytes were chromatid-type breaks or exchanges. Among chromosome-type aberrations, double fragments for exceeded chromosome exchanges. This spectrum of structural aberrations differed markedly from what was previously observed in one-cell embryos conceived by DEB-treated sperm, where 97% were chromosome-type aberrations and 40% were dicentrics or translocations. This difference suggests that chromosome damage in one-cell embryos can be fixed by different mutagenic pathways influenced by the targeted gamete and its specific chromatin configuration. After exposure to the same dose, oocytes transmitted to one-cell embryos between 4 and 8 times fewer aberrations than DEB-treated sperm. While the rate of aberration induction suggests that female germ cells may be less at risk than mature sperm, especially at low-dose levels, the higher threshold for reproductive toxicity observed in female than in male mice may justify inclusion of data on female germ cell mutagenicity in the genetic risk assessment of butadiene exposure.