Ilse-Dore Adler

In vivo rodent erythrocyte micronucleus assay. II. Some aspects of protocol design including repeated treatments, integration with toxicity testing, and automated scoring.

An expert working group on the in vivo micronucleus assay, formed as part of the International Workshop on Genotoxicity Test Procedures (IWGTP), discussed protocols for the conduct of established and proposed micronucleus assays at a meeting held March 25–26, 1999 in Washington, DC, in conjunction with the annual meeting of the Environmental Mutagen Society. The working group reached consensus on a number issues, including: (1) protocols using repeated dosing in mice and rats; (2) integration of the (rodent erythrocyte) micronucleus assay into general toxicology studies; (3) the possible omission of concurrently‐treated positive control animals from the assay; (4) automation of micronucleus scoring by flow cytometry or image analysis; (5) criteria for regulatory acceptance; (6) detection of aneuploidy induction in the micronucleus assay; and (7) micronucleus assays in tissues (germ cells, other organs, neonatal tissue) other than bone marrow. This report summarizes the discussions and recommendations of this working group. In the classic rodent erythrocyte assay, treatment schedules using repeated dosing of mice or rats, and integration of assays using such schedules into short‐term toxicology studies, were considered acceptable as long as certain study criteria were met. When the micronucleus assay is integrated into ongoing toxicology studies, relatively short‐term repeated‐dose studies should be used preferentially because there is not yet sufficient data to demonstrate that conservative dose selection in longer term studies (longer than 1 month) does not reduce the sensitivity of the assay. Additional validation data are needed to resolve this point. In studies with mice, either bone marrow or blood was considered acceptable as the tissue for assessing micronucleus induction, provided that the absence of spleen function has been verified in the animal strains used. In studies with rats, the principal endpoint should be the frequency of micronucleated immature erythrocytes in bone marrow, although scoring of peripheral blood samples gives important supplementary data about the time course of micronucleus induction. When dose concentration and stability are verified appropriately, concurrent treatment with a positive control agent is not necessary. Control of staining and scoring procedures can be obtained by including appropriate reference samples that have been obtained from a separate experiment. For studies in rats or mice, treatment/sampling regimens should include treatment at intervals of no more than 24 hr (unless the test article has a half‐life of more than 24 hr) with sampling of bone marrow or blood, respectively, within 24 or 40 hr after the last treatment. The use of a DNA specific stain is recommended for the identification of micronuclei, especially for studies in the rat. In the case of a negative assay result with a non‐toxic test article, it is desirable that systemic exposure to the test article is demonstrated. The group concluded that successful application of automated scoring by both flow cytometry and image analysis had been achieved, and defined criteria that should be met if automated scoring is employed. It was not felt appropriate to attempt to define specific recommended protocols for automated scoring at the present time. Other issues reviewed and discussed by the working group included micronucleus assays that have been developed in a number of tissues other than bone marrow. The group felt that these assays were useful research tools that could also be used to elucidate mechanisms in certain regulatory situations, but that these assays had not yet been standardized and validated for routine regulatory application. Environ. Mol. Mutagen. 35:234–252, 2000

Comparative cytogenetic study after treatment of mouse spermatogonia with mitomycin C

Abstract Male (101 × C 3 H)F 1 hybrid mice, 10–12 weeks old, were injected i.p. with single doses of 2.5, 3.75 or 5.0 mg/kg of mitomycin C (MC). Spermatogonia were sample for mitotic chromosome analyses 6, 18 or 24 h after treatment. Spermatocytes were sample for meiotic chromosome analyses 50 or 60 days after treatment. The maximal yield of chromatid-type aberrations induced in spermatogonia was found 24 h after treatment with 5.0 mg/kg of MC. More than 50% of the cells carried at least one chromatid exchange. The majority (90%) of these were whole-arm exchanges derived from breaks in the centromeric heterochromatin. No translocation multivalents were found in spermatocytes analysed 50 or 60 days after treatment. The discrepancy between the presence of many symmetrical exchanges in spermatogonia and the absence of translocation multivalents in primary spermatocytes may be result of insensitivity of the stem cell spermatogonia against exchange induction by MC or of complete germinal selection against induced translocations before and/or during early meiosis. However, the possibility of missing translocations due to whole-arm exchanges in acrocentric chromosomes during the analysis of diakineses-metaphases I is also discussed. It is emphasized that comparisons of chromatid exchange frequencies in spermatogonia with the yield of translocation multivalents in spermatocytes descended from these spermatogonia as opposed to those from stem cells might provide an estimate of pre-diakinesis germinal selection against chromatid exchanges or the resulting translocations. This estimate is important for the quantitative evaluation of the genetic risk from environmental mutagens.

Trichlorfon exposure, spindle aberrations and nondisjunction in mammalian oocytes

Abstract. Consumption of trichlorfon-poisoned fish by women in a small Hungarian village has been associated with trisomy resulting from an error of meiosis II in oogenesis. We therefore examined mouse oocytes exposed for 3 h during fertilization to 50 µg/ml trichlorfon. Spindle morphology was not visibly altered by the pesticide. Chromosomes segregated normally at anaphase II with no induction of aneuploidy. However, formation of a spindle was disturbed in many oocytes resuming meiosis I in the presence of trichlorfon. In spite of the spindle aberrations and the failure of bivalents to align properly at the equator, oocytes did not become meiotically arrested but progressed to metaphase II. At this stage, spindles were highly abnormal, and chromosomes were often totally unaligned, unattached or dispersed on the elongated and disorganized spindle. By causing spindle aberrations and influencing chromosome congression, trichlorfon appears, therefore, to predispose mammalian oocytes to random chromosome segregation, especially when they undergo a first division and develop to metaphase II during exposure. This is the first case in which environmentally induced human trisomy can be correlated with spindle aberrations induced by chemical exposure. Our observations suggest that oocytes may not possess a checkpoint sensing displacement of chromosomes from the equator at meiosis I and may therefore be prone to nondisjunction.

Mutagenicity of 1,3-butadiene inhalation in somatic and germinal cells of mice

Inhalation exposure of mice to 50, 200, 500 or 1300 ppm of 1,3-butadiene for 6 h per day for 5 consecutive days caused micronuclei in mouse bone marrow and peripheral blood erythrocytes. The dose response was non-linear. The slope of the curve flattened with increasing exposure concentration. Coat color spots were found in the mouse spot test after exposure of pregnant females on pregnancy days 8-12 to 500 ppm of 1,3-butadiene. Dominant lethal mutations were induced in spermatozoa and late spermatids after exposure of male mice to 1300 ppm with the 5-day exposure regimen. Thus, in the mouse 1,3-butadiene is a somatic and germ cell mutagen.

Induction of aneuploidy in male mouse germ cells detected by the sperm–FISH assay: a review of the present data base

Multicolour fluorescence in situ hybridization (FISH) with chromosome-specific DNA-probes can be used to assess aneuploidy (disomy) and diploidy in sperm of any species provided the DNA-probes are available. In the present EU research project, DNA-probes for mouse chromosomes 8, X and Y were employed each labelled with different colours. Male mice were treated with the test chemicals and sperm were sampled from the Caudae epididymes 22-24 days later to allow spermatocytes exposed during meiosis to develop into mature sperm. At present, the data base comprises 10 chemicals: acrylamide (AA), carbendazim (CB), colchicine (COL), diazepam (DZ), griseofulvin (GF), omeprazole (OM), taxol (TX), thiobendazole (TB), trichlorfon (TF) and vinblastine (VBL). Of these, COL and TF induced disomic sperm only. DZ and GF induced disomic and diploid sperm, while CB and TB induced diploid sperm only. VBL gave contradictory results in repeated experiments in an inter-laboratory comparison. AA, OM and TX did not induce an increase in disomic or diploid sperm at the doses used. The induction of aneuploidy by DZ was also tested in humans. Sperm samples from patients after attempted suicide and from patients with chronic Valium((R)) abuse were evaluated using human DNA-probes specific for chromosomes 1,16, 21, X and Y. A quantitative comparison between mouse and man indicates that male meiosis in humans is 10-100 times more sensitive than in mice to aneuploidy induction by DZ. The positive response of mice to TF supports the hypothesis by Czeizel et al. [Lancet 341 (1993) 539] that TF may be causally related to the occurrence of congenital abnormality clusters in a Hungarian village.

Synopsis of the in vivo results obtained with the 10 known or suspected aneugens tested in the CEC collaborative study

The synopsis of the in vivo test results in the first collaborative CEC Aneuploidy Project with 10 selected chemicals, colchicine (COL), econazole (EZ), chloral hydrate (CH), hydroquinone (HQ), diazepam (DZ), thiabendazole (TB), cadmium chloride (CD), thimerosal (TM), pyrimethamine (PY) and vinblastine (VBL), allowed several conclusions. (1) The spindle poisons, COL and VBL, were positive in all bone marrow and germ cell tests; (2) the clastogen HQ also induced aneuploidy in somatic and germinal cells; (3) the other seven compounds gave contradictory results either between laboratories or between test systems which require further experimental clarification; (4) CREST labeling or in situ hybridization for centromere identification showed about 70% fluorescent signals in micronuclei induced by COL or VBL but only about 15% in HQ induced micronuclei; (5) the tests for induction of a delay in cell division progression can be recommended as a prescreen for possible aneugens; (6) all test methods applied in these experiments require standardization with respect to sample size, sampling times and statistical treatment of the data. A second CEC Aneuploidy Programme has started recently to answer some of the questions raised by the first study regarding tissue and sex specificities.

The present lack of evidence for unique rodent germ-cell mutagens

Six chemicals, diethylhexyl phthalate (DEHP), ethanol, cyclohexylamine (CHA), sodium saccharin (NaS), cadmium chloride (CdCl2) and triflupromazine (TFP), were suggested to be unique germ-cell mutagens (Auletta and Ashby, 1988) by the GeneTox Workgroups of the U.S. Environmental Protection Agency (EPA). If this is a correct classification it would have major consequences when screening for mutagenicity and when labelling genotoxic substances. However, our re-evaluation of the GeneTox literature, including some more recent publications, has failed to find substantive evidence that any of these chemicals have been unequivocally established as having unique mutagenic activity in germ cells. For DEHP, NaS and TFP the evidence for genotoxic/mutagenic effects is questionable, in both germinal and somatic cells. Ethanol and CdCl2 showed clastogenic activity, but it was not restricted to germ cells. Both, ethanol and cadmium salts, appear to induce aneuploidy. The unconfirmed clastogenic effect of CHA was restricted to rats, but it occurred in both bone marrow and spermatogonia. Therefore, the general observation that rodent germ-cell mutagens are also genotoxic in somatic cells in vivo (Brusick, 1980; Holden, 1982) remains valid.

Aberration induction by mitomycin C in early primary spermatocytes of mice

MC is well known to induce dominant lethal mutations in mouse spermatocytes. Tests were done to determine whether chromosomal aberrations could be identified in spermatocytes as being responsible for the dominant lethal effects. Male mice were treated with single doses of MC during DNA synthesis preceding meiosis and during early prophase of meiosis. Simultaneous labeling was performed to identify cells that were in S-phase during the time of treatment. Diakineses-metaphases I were analyzed for the occurrence of univalents, gaps, fragments and rearrangements. The frequencies of cells with aberrations increased with dose and time after treatment. Maximal values were obtained after 12 days, indicating that MC was most effective in cells undergoing DNA replication. 95% of these cells were labeled. The majority of aberrant cells contained one or more fragments. These cells will lead to dominant lethality of the zygotes after fertilization. Cells with rearrangements occurred 11 and 12 days after treatment. These cells can develop into sperm carrying a reciprocal translocation which would then give rise to semi-sterile progeny after fertilization. Further investigations are needed to study the transmission of rearrangements observed in primary spermatocytes.

Recommendations for statistical designs of in vivo mutagenicity tests with regard to subsequent statistical analysis

A workshop was held on September 13 and 14, 1993, at the GSF, Neuherberg, Germany, to start a discussion of experimental design and statistical analysis issues for three in vivo mutagenicity test systems, the micronucleus test in mouse bone marrow/peripheral blood, the chromosomal aberration tests in mouse bone marrow/differentiating spermatogonia, and the mouse dominant lethal test. The discussion has now come to conclusions which we would like to make generally known. Rather than dwell upon specific statistical tests which could be used for data analysis, serious consideration was given to test design. However, the test design, its power of detecting a given increase of adverse effects and the test statistics are interrelated. Detailed analyses of historical negative control data led to important recommendations for each test system. Concerning the statistical sensitivity parameters, a type I error of 0.05 (one tailed), a type II error of 0.20 and a dose related increase of twice the background (negative control) frequencies were generally adopted. It was recommended that sufficient observations (cells, implants) be planned for each analysis unit (animal) so that at least one adverse outcome (micronucleus, aberrant cell, dead implant) would likely be observed. The treated animal was the smallest unit of analysis allowed. On the basis of these general consideration the sample size was determined for each of the three assays. A minimum of 2000 immature erythrocytes/animal should be scored for micronuclei from each of at least 4 animals in each comparison group in the micronucleus assays. A minimum of 200 cells should be scored for chromosomal aberrations from each of at least 5 animals in each comparison group in the aberration assays. In the dominant lethal test, a minimum of 400 implants (40-50 pregnant females) are required per dose group for each mating period. The analysis unit for the dominant lethal test would be the treated male unless the background frequency of dead implants (DI) is so low that multiple males would need to be integrated to meet the minimum observation of one adverse outcome (DI) per analysis unit. A three-step strategy of data analysis was proposed for the cytogenetic assays. Use of negative historical controls was allowed in certain circumstances for interpretation of results from micronucleus tests and chromosomal aberration tests.

1,3-Butadiene working group report

During the Workshop in North Carolina, the in vivo metabolism, adduct formation and genotoxicity data available from rodent and human exposure to 1,3-butadiente (BD) were reviewed and they are summarized in the present report. BD is metabolized by cytochrome P-450-dependent monoxygenases to the primary metabolite 1,2-epoxybutene-3 (epoxybutene, EB). EB is subjected to further metabolism: oxidation to 1,2:3,4-diepoxybutane (DEB), hydrolysis to 3-butene-1,2-diol and conjugation to glutathione. The first pathway seems to prevail in mice while the latter is characteristic for rats and possibly for humans. Species differences exist in adduct formation of the monoepoxide to hemoglobin, for which the following pattern has been found: mice > rats > humans. Genotoxity of BD was found in mice with all applied tests; however, negative results were obtained in rats. In exposed humans, the cytogenetic studies in peripheral blood lymphocytes did not show genotoxic effects, although one report described elevated hprt variant levels in peripheral blood lymphocytes of exposed workers. It was concluded that the presently available data are insufficient for the application of the parallelogram model to estimate genetic risk for humans. As an alternative approach, a tentative estimate of the doubling dose for induction of hprt mutations in somatic cells of mice and men was performed and the calculated values were surprisingly similar, i.e. 9000 ppmh. However, this estimate is burdened with a number of caveats which were discussed in detail. The working group identified a series of urgent research needs to provide the appropriate data for the application of the parallelogram model, such as identification of metabolic pathways in different rodent species and humans, metabolic studies in mice, rats and humans considering metabolic polymorphisms, studies of adducts to DNA and hemoglobin especially of DEB and other butadiene metabolites in rodents and humans, studies of mutational spectra (mutational fingerprinting) in somatic and germinal cells, confirmation of the human hprt mutation data, conformation of the rodent malformation data, dose-response studies in rodent germ cell tests and studies on repair kinetics of mono-adducts induced by EB as opposed to repair of cross-links produced by DEB. Finally, it was suggested that the original parallelogram consisting of data from somatic cell studies in rodents and humans plus studies of heritable effects in rodents to extrapolate to germ cell risk for humans should be supplemented with studies in sperm of experimental animals and exposed men.