A comparative study on selected chemical carcinogens for chromosome malsegregation, mitotic crossing-over and forward mutation induction in Aspergillus nidulans

Mode of action of dieldrin-induced liver tumors: application to human risk assessment

Dieldrin is an organochlorine insecticide that was widely used until 1970 when its use was banned because of its liver carcinogenicity in mice. Several long-term rodent bioassays have reported dieldrin to induce liver tumors in in several strains of mice, but not in rats. This article reviews the available information on dieldrin liver effects and performs an analysis of mode of action (MOA) and human relevance of these liver findings. Scientific evidence strongly supports a MOA based on CAR activation, leading to alterations in gene expression, which result in increased hepatocellular proliferation, clonal expansion leading to altered hepatic foci, and ultimately the formation of hepatocellular adenomas and carcinomas. Associative events include increased liver weight, centrilobular hypertrophy, increased expression of Cyp2b10 and its resulting increased enzymatic activity. Other associative events include alterations of intercellular gap junction communication and oxidative stress. Alternative MOAs are evaluated and shown not to be related to dieldrin administration. Weight of evidence shows that dieldrin is not DNA reactive, it is not mutagenic, and it is not genotoxic in general. Furthermore, activation of other pertinent nuclear receptors, including PXR, PPARα, AhR, and estrogen are not related to dieldrin-induced liver tumors nor is there liver cytotoxicity. In previous studies, rats, dogs, and non-human primates did not show increased cell proliferation or production of pre-neoplastic or neoplastic lesions following dieldrin treatment. Thus, the evidence strongly indicates that dieldrin-induced mouse liver tumors are due to CAR activation and are specific to the mouse, which are qualitatively not relevant to human hepatocarcinogenesis. Thus, there is no carcinogenic risk to humans. This conclusion is also supported by a lack of positive epidemiologic findings for evidence of liver carcinogenicity. Based on current understanding of the mode of action of dieldrin-induced liver tumors in mice, the appropriate conclusion is that dieldrin is a mouse specific liver carcinogen and it does not pose a cancer risk to humans.

Mutagenic effects of a commercial glyphosate-based herbicide formulation on the soil filamentous fungus Aspergillus nidulans depending on the mode of exposure

Glyphosate-based herbicides (GBH) are the most used pesticides worldwide. This widespread dissemination raises the question of non-target effects on a wide range of organisms, including soil micro-organisms. Despite a large body of scientific studies reporting the harmful effects of GBHs, the health and environmental safety of glyphosate and its commercial formulations remains controversial. In particular, contradictory results have been obtained on the possible genotoxicity of these herbicides depending on the organisms or biological systems tested, the modes and durations of exposure and the sensitivity of the detection technique used. We previously showed that the well-characterized soil filamentous fungus Aspergillus nidulans was highly affected by a commercial GBH formulation containing 450 g/L of glyphosate (R450), even when used at doses far below the agricultural application rate. In the present study, we analysed the possible mutagenicity of R450 in A. nidulans by screening for specific mutants after different modes of exposure to the herbicide. R450 was found to exert a mutagenic effect only after repeated exposure during growth on agar-medium, and depending on the metabolic status of the tested strain. The nature of some mutants and their ability to tolerate the herbicide better than did the wild-type strain suggested that their emergence may reflect an adaptive response of the fungus to offset the herbicide effects. The use of a non-selective molecular approach, the quantitative random amplified polymorphic DNA (RAPD-qPCR), showed that R450 could also exert a mutagenic effect after a one-shot overnight exposure during growth in liquid culture. However, this effect was subtle and no longer detectable when the fungus had previously been repeatedly exposed to the herbicide on a solid medium. This indicated an elevation of the sensitivity threshold of A. nidulans to the R450 mutagenicity, and thus confirmed the adaptive capacity of the fungus to the herbicide.

Genotoxicity of heptachlor and heptachlor epoxide in human TK6 lymphoblastoid cells

The genotoxic potential of the organochlorine insecticides heptachlor (HC) and its metabolite heptachlor epoxide (HCE) has been evaluated in TK6 cells, a well-established human lymphoblastoid cell line. Genotoxicity has been determined by scoring the induction of DNA breaks in the comet assay and by measuring the frequency of micronuclei (MN) in binucleated cells. The results indicate that both compounds are able to induce significant increases in the percentage of DNA in the tail, the parameter used in the comet assay, with a direct dose-response relationship. Nevertheless, both compounds were unable to induce an increase in the frequency of MN. The comet assay measures primary DNA damage, while the induction of MN measures fixed damage. Thus, our results would suggest that the DNA damage induced by the two insecticides is not fixed as chromosome damage, which would be detectable by means of the MN assay (chromosome breaks and aneuploidy).

ATSDR evaluation of health effects of benzene and relevance to public health

As part of its mandate, the Agency for Toxic Substances and Disease Registry (ATSDR) prepares toxicological profiles on hazardous chemicals found at Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA) National Priorities List (NPL) sites that have the greatest public health impact. These profiles comprehensively summarize toxicological and environmental information. This article constitutes the release of portions of the Toxicological Profile for Benzene. The primary purpose of this article is to provide public health officials, physicians, toxicologists, and other interested individuals and groups with an overall perspective on the toxicology of benzene. It contains descriptions and evaluations of toxicological studies and epidemiological investigations and provides conclusions, where possible, on the relevance of toxicity and toxicokinetic data to public health.

Recombinogenic activity of 10 chemical compounds in male germ cells of Drosophila melanogaster

The Drosophila melanogaster male germ cells are sensitive to the recombinogenic activity of chemical compounds. In our experiments, we have employed four recessive markers located on the 2nd chromosome: dumpy (dp, 13.0), black (b, 48.5), cinnabar (cn, 57.5), and brown (bw, 104.5); b and cn flank the centromere. Three-day-old larvae, heterozygous for these markers, were treated chronically by oral administration with the test compounds. The chemicals already shown to be positive or negative in the assay systems to test chemical agents in D. melanogaster are three carcinogens (4-nitroquinoline N-oxide, hydroxylamine HCl, and acrylamide), four herbicides (maleic hydrazide, alachlor, trifluralin, and amitrol), and three insecticides (endrin, piperonyl butoxide, and allethrin). In our study, some compounds induced recombinogenic effects in Drosophila premeiotic male germ cells, and comparison of our results with those reported in the literature with the Drosophila wing somatic mutation and recombination assay showed that the somatic cells and the germinal cells have a differential response to the defined compounds.

Genotoxicity of benzene and its metabolites

The potential role of genotoxicity in human leukemias associated with benzene (BZ) exposures was investigated by a systematic review of over 1400 genotoxicity test results for BZ and its metabolites. Studies of rodents exposed to radiolabeled BZ found a low level of radiolabel in isolated DNA with no preferential binding in target tissues of neoplasia. Adducts were not identified by 32P-postlabeling (equivalent to a covalent binding index <0.002) under the dosage conditions producing neoplasia in the rodent bioassays, and this method would have detected adducts at 1/10,000th the levels reported in the DNA-binding studies. Adducts were detected by 32P-postlabeling in vitro and following high acute BZ doses in vivo, but levels were about 100-fold less than those found by DNA binding. These findings suggest that DNA-adduct formation may not be a significant mechanism for BZ-induced neoplasia in rodents. The evaluation of other genotoxicity test results revealed that BZ and its metabolites did not produce reverse mutations in Salmonella typhimurium but were clastogenic and aneugenic, producing micronuclei, chromosomal aberrations, sister chromatid exchanges and DNA strand breaks. Rodent and human data were compared, and BZ genotoxicity results in both were similar for the available tests. Also, the biotransformation of BZ was qualitatively similar in rodents, humans and non-human primates, further indicating that rodent and human genotoxicity data were compatible. The genotoxicity test results for BZ and its metabolites were the most similar to those of topoisomerase II inhibitors and provided less support for proposed mechanisms involving DNA reactivity, mitotic spindle poisoning or oxidative DNA damage as genotoxic mechanisms; all of which have been demonstrated experimentally for BZ or its metabolites. Studies of the chromosomal translocations found in BZ-exposed persons and secondary human leukemias produced by topoisomerase II inhibitors provide some additional support for this mechanism being potentially operative in BZ-induced leukemia.

Evaluation of genotoxicity of captan, maneb and zineb in the wing spot test of Drosophila melanogaster: role of nitrosation

The wing spot test in Drosophila melanogaster is a suitable system for the analysis of genotoxic activity of compounds that need metabolic transformation to render them active. We have analysed the genotoxicity of three fungicides for which it was reported that the metabolic processes taking place in vivo may determine their activity. The compounds analysed are captan, maneb, zineb and ethylenethiourea (ETU) (a metabolic derivative of ethylenebisdithiocarbamates like maneb and zineb). We have also evaluated the ability of ETU to form genotoxic derivatives in vivo analysing this compound in combined treatments with sodium nitrite. Both standard and high bioactivation NORR strains have been used. Captan, usually considered a mutagen in vitro but a non-mutagen in vivo, gave negative results in the wing spot test with both crosses. Positive results were obtained for maneb in the standard cross and for ETU in both the standard and the high bioactivation cross. The genotoxicities of maneb and ETU were higher when treatments were made on media in which nitrosation is favoured. A low absorption of the fungicide and an inefficient availability of the compound in the target may explain negative results obtained with zineb in both crosses. The results obtained in this study with the wing spot test demonstrate once again the suitability of this in vivo assay, in which absorption, distribution and metabolism processes take place, for the evaluation of genotoxicity of compounds to which humans are exposed.

The rodent carcinogens 1,4-dioxane and thiourea induce meiotic non-disjunction in Drosophila melanogaster females

The ability of the rodent carcinogens 1,4-dioxane (DX) and thiourea (TU) to induce meiotic non-disjunction (ND) was assessed in 3- and 6-day-old Drosophila melanogaster females. The chemicals were administered orally and three 24 h and one 48 h broods were obtained after mating, to sample oocytes treated in increasingly earlier stages of development. The broods represent mainly mature oocytes (brood I), nearly mature oocytes (brood II), early oocytes (brood III) and very early oocytes (brood IV). The toxicity of DX increased with dose (1% (not toxic), 1.5, 2, 3, 3.5%) as well as a reduction in fecundity which was moderate. Induction of ND in mature oocytes was positive with 2, 3 and 3.5% concentrations and was not related to dose. In immature oocytes it was also positive though already at the lowest concentration tested (1%), suggesting a sensitivity higher than that of mature oocytes. TU at 0.10-10%, did not affect viability, but since fecundity was seriously impaired at high doses, ND was not assessed beyond the 1.5% concentration. TU also induced ND in mature and in immature oocytes; neither a threshold nor a dose effect was detected. The response of mature oocytes was lower than that of immature oocytes. TU induced increases of ND in the earliest cells tested in a more consistent fashion than DX. The data clearly show that both chemicals induced ND in mature oocytes and in the three subsets in which immature oocytes were fractionated. Though toxicity may play a significant unspecific role in the induction of chromosome malsegregation by DX and TU, the induction of ND at low doses, moderately toxic to the oocytes, suggests that the interaction with specific targets contributed to the results obtained.

Genotoxicity testing of five herbicides in the Drosophila wing spot test

Four triazine herbicides: amitrole, metribuzin, prometryn and terbutryn, and the bipyridal compound diquat dibromide have been evaluated for genotoxicity in the wing somatic mutation and recombination test of Drosophila melanogaster, following standard procedures. Third-instar larvae trans-heterozygous for the third chromosome recessive markers multiple wing hairs (mwh) and flare-3 (flr(3)) were chronically fed with different concentrations of the test compounds. Feeding ended with pupation of the surviving larvae. Genetic changes induced in somatic cells of the wing's imaginal discs lead to the formation of mutant clones on the wing blade. Point mutation, chromosome breakage and mitotic recombination produce single spots; while twin spots are produced only by mitotic recombination. Exposure to 0.5 mM and 1 mM of amitrole clearly increased the frequency of small single, large single and total spots. Terbutryn, at the concentration of 5 mM, induced a slight increase in the frequency of small single and total spots, but this result could be false positive. The other three herbicides tested did not show any genotoxic effect. When heterozygous larvae for mwh and the multiple inverted TM3 balancer chromosomes were treated, significant increases in the frequency of mutant spots were only detected for amitrole. The observed spot frequencies were lower than those found in mwh/flr(3)50%) of the total spot induction was due to mitotic recombination.

Comparative study on germ cell mutation induced by urethane (ethyl carbamate) gas and X-rays in Drosophila melanogaster

Although its mutagenicity has not been confirmed in mouse germ cells, urethane (ethyl carbamate) gas induces a significant increase of X-linked recessive lethal mutations in the germ cells of Drosophila melanogaster. The mutation frequency increased as the exposure time was changed from 3.5 to 5.5 h. Mutations were also induced by X-rays (20 to 40 Gy) and N-methyl-N-nitrosourea (MNU) (0.06 to 0.10%). However, no significant increase of chromosomal changes (partial loss of the Y chromosome, total loss of X or Y, and translocations) was produced by urethane, although these were readily induced by X-rays. There were large and significant increase in chromosomal changes caused by X-rays (20 Gy) compared to urethane (5.5 h) or MNU (0.06%). In contrast, there were no substantial differences among these three treatments as regards recessive lethal mutations. Urethane-induced DNA lesions detected as recessive lethals appear to be intragenic mutations. Complementation analysis with 15 reference single-site loci (cistrons) in the zeste-white region of the X chromosome revealed that 29 of 723 urethane-induced recessive lethals were located in the zeste-white region and all were restricted to a single locus. However, among 28 of 890 X-ray-induced lethals, 2 were non-complementary to 2 or 3 adjacent loci, indicating deletions encompassing 2 or 3 loci. In addition, 3 of these lethal chromosomes included mutations outside the zeste-white region. Another difference between urethane and X-rays was in the distribution of mutation sites. Urethane-induced mutations were strikingly non-random with two hot spots at zw-1 and zw-2, whereas the distribution of X-ray-induced mutations was more nearly random.

Cytogenotoxicities of sublimed urethane gas to the mouse embryo

Urethane (ethyl carbamate) which has long been used for commonly used drugs and has proven to be useful in the formation of products in every-day use, is volatile, and small amounts sublime spontaneously. Pregnant ICR mice were maintained in the vinyl chamber (45 liter) which was ventilated 4 times per hour. To inhale urethane gas, air was passed first through a glass bottle containing 500 g of crystalline urethane and then into the vinyl chamber. Concentration of the sublimed urethane gas in the chamber was 1.28 +/- 0.08 mg/l, and sublimed urethane gas produced significantly high incidence of chromosomal aberrations in the cells of whole embryo, when mice inhaled it for 48 h from day 9 to day 11 of pregnancy. High and significant incidence of chromosomal aberrations (36.0%) was detected in the embryo 3 h after urethane gas inhalation, but decreased to 5.3% at 24 h after exposure and showed no significant differences from controls after 48 h, while the incidence in bone marrow cells from the adult (pregnant) mice was lower (21.5%) at 3 h after exposure but a significant increase remained until 72 h after exposure. A majority of chromosomal aberrations was chromatid types. As a consequence of cellular damages by urethane gas inhalation during pregnancy, significantly high incidence of fetal deaths and congenital malformations (cleft palate, polydactyly, tail anomaly etc.) was induced in the offspring. Thus, we must be aware of the risk of volatile chemicals, because it is difficult to perceive and avoid hazardous exposure via respiration.

Chloral hydrate is recombinogenic in the wing spot test in Drosophila melanogaster

In order to characterise the response of the wing spot test in Drosophila melanogaster to the effects of compounds with known aneugenic properties, experiments were performed with chloral hydrate (CH). Following chronic exposure of 72-h-old larvae to rising concentrations of CH, significant increases in the frequency of small (1-2 cells) single spots were observed. Comparison of results obtained in parallel from the wings of marker-trans-heterozygous individuals and individuals heterozygous for one of two different balancer chromosomes suggests that practically all the single clones originated from recombinational events. Twin clone frequencies were, however, only weakly affected. These results are discussed with reference to the literature regarding the effects of CH in different experimental systems and to the characteristics of Drosophila as a tester organism.

Ethylene thiourea (ETU). A review of the genetic toxicity studies

Ethylene thiourea (ETU) is a common contaminant, metabolite and degradation product of the fungicide class of ethylene bisdithiocarbamates (EBDCs); as such, they present possible exposure and toxicological concerns to exposed individuals. ETU has been assayed in many different tests to assess genotoxicity activity. While a great number of negative results are found in the data base, there is evidence that demonstrates ETU is capable of inducing genotoxic endpoints. These include responses for gene mutations (e.g. Salmonella), structural chromosomal alterations (e.g. aberrations in cultured mammalian cells as well as a dominant lethal assay) and other genotoxic effects (e.g. bacterial rec assay and several yeast assays). It is important to consider the magnitude of the positive responses as well as the concentrations/doses used when assessing the genotoxicity of ETU. While ETU induces a variety of genotoxic endpoints, it does not appear to be a potent genotoxic agent. For example, it is a weak bacterial mutagen in the Salmonella assay without activation in strain TA1535 at concentrations generally above 1000 micrograms/plate. Weak genotoxic activity of this sort is usually observed in most of the assays with positive results. Since ETU does not appear very potent and is not extremely toxic to test cells and organisms, it is not surprising to find that ETU does not produce consistent effects in many of the assays reviewed. Consequently, in many instances, mixed results for the same assay type are reported by different investigators, but as reviewed herein, these results may be dependent upon the test conditions in each individual laboratory. A primary shortcoming with many of the reported negative results is that the concentrations or doses used are not high enough for an adequate test for ETU activity. There are also problems with many of the negative assays generally in protocol or reporting, particularly with the in vivo studies (e.g. inappropriate sample number and/or sampling times; inadequate top dose employed). Overall, while ETU does not appear to be a potent genotoxic agent, it is capable of producing genotoxic effects (e.g. gene mutations, structural chromosomal aberrations). This provides a basis for weak genotoxic activity by ETU. Furthermore, based on a suggestive dominant lethal positive result, there may be a concern for heritable effects. Due to the many problems with the conduct and assessment of the in vivo assays, it is worth repeating in vivo cytogenetic assays and a dominant lethal assay (with acceptable test procedures and data generation) to determine if these results would continue to support a heritable mutagenicity concern.

A survey of EPA/OPP and open literature data on selected pesticide chemicals tested for mutagenicity. I. Introduction and first ten chemicals

Parties interested in registering a pesticide chemical with the U.S. Environmental Protection Agency's (USEPA's) Office of Pesticide Programs (OPP) must submit toxicity information to support the registration. Mutagenicity data are a part of the required information that must be submitted. This information is available to the public via Freedom of Information requests to the OPP. However, it is felt that this information would be more effectively and widely disseminated if presented in a published medium. Beginning with this publication, sets of mutagenicity data on pesticide chemicals will be periodically published in the Genetic Activity Profile (GAP) format. In addition, mutagenicity data extracted from the currently available open literature is also presented to provide a more complete database and to allow comparisons between the OPP-submitted data and other publicly available information.

The genotoxicity of nitrilotriacetic acid (NTA) in a somatic mutation and recombination test in Drosophila melanogaster

The genotoxicity of a chelating agent, the trisodium salt of nitrilotriacetic acid (NTA), was assessed in a somatic mutation and recombination test (SMART) in Drosophila melanogaster employing the wing hair markers mwh and flr3. The experiments were performed in parallel in two different laboratories (Padua, Italy and Schwerzenbach, Switzerland). The effectively absorbed doses of NTA, which was administered by feeding to larvae, were determined by a sensitive method employing [3H]leucine which allowed individual consumption levels to be measured. The particular pattern of clone induction produced by this compound suggests that NTA is active in inducing mitotic recombination and possibly aneuploidy in somatic cells of Drosophila. This is discussed in relation to the data present in the literature regarding the genotoxicity of NTA in a variety of experimental systems.

Mutagenicity, metabolism, and DNA interactions of urethane

Urethane, a known animal carcinogen, has been the subject of intensive research efforts spanning 40 years. Recent concerns have focused on the presence of urethane in a variety of fermented foods and alcoholic beverages, although no epidemiological studies or human case reports have been published. Much information is available about the mutagenesis, metabolism, and DNA interactions of urethane in experimental systems. Urethane is generally not mutagenic in bacteria although in some instances it acts as a weak mutagen. Urethane is not mutagenic in Nuerospora but is weakly mutagenic in Saccharomyces. Drosophila appear to be the only organisms that consistently give positive mutagenic results with urethane, but its mutagenicity is weak and in many cases shows no clear dose dependence. Urethane is a good clastogen in mammalian somatic cells in vivo, but it shows variable results with cells in vitro. It efficiently induces sister chromatid exchanges in a variety of cells. Mammalian spermatogenic cells are insensitive to the induction of specific locus and dominant lethal mutations by urethane. Mutational synergism has been reported to occur between ethyl methanesulfonate and urethane when administered two generations apart, and some investigators have suggested possible synergism for cancer-causing mutations in mice exposed to X-rays and urethane one generation apart. These studies are controversial and have not been confirmed. Studies on the induction of cancer-causing dominant mutations by urethane are at variance with results from extensive studies with the specific locus test in mice. Urethane studies with the unscheduled DNA synthesis assay in mouse spermatogenic cells and with the sperm abnormality test have given negative results. Urethane is rapidly and evenly distributed in the body. The rate of elimination of urethane from plasma is a saturable process and varies according to the strain and age of the animal. Recent studies have concentrations similar to those in wine, ethanol inhibits the tissue distribution of urethane in mice. These results are important because they suggest a lower carcinogenic/mutagenic risk than expected from exposure to urethane in alcoholic beverages. Although research on the metabolic activation of urethane has been extensive, no conclusive results have been obtained about its active metabolite, at one time thought to be N-hydroxyurethane. More recently, it has been postulated that urethane is activated to vinyl carbamate and that this metabolite is capable of reacting with DNA.(ABSTRACT TRUNCATED AT 400 WORDS)

Quantitative approaches for assessing chromosome loss in Saccharomyces cerevisiae: general methods for analyzing downturns in dose response

Statistical methods are considered for analysis of data arising from a mitotic chromosome loss assay in Saccharomyces cerevisiae strain D61.M. The methods make use of reproducibility trial data from the assay (presented herein) and previous data, which suggest a unimodal, 'umbrella-patterned' dose response. Computer simulations are employed to illustrate the operating characteristics of the umbrella response methods. These methods are generally applicable to any toxicity assay that exhibits a downturn in dose response. Experimental design considerations are also discussed. These include applications of 2-stage sampling rules to first gauge the dose window of peak response, then test if the response deviates significantly from untreated levels.

Lack of induction of somatic aneuploidy in the mouse by nitrilotriacetic acid (NTA)

Nitrilotriacetic acid (NTA) was tested for the induction of aneuploidy in mouse bone marrow cells. Doses of 138 or 275 mg/kg of body weight were intraperitoneally injected 24 h after implantation of a bromodeoxyuridine tablet. Cell-replication kinetics was assessed by comparing the relative percentages of first, second and third metaphases in control and treated samples. The hyperploidy incidence was estimated in second metaphases only, together with the SCE/cell level. Mice injected with 1.8 mg/kg vinblastine (VBL) were used as positive controls. A slight delay of cell cycle was induced by NTA, as shown by regression analysis applied to average generation time values. No increase over the control level was observed for hyperploidy or SCE induction in NTA-treated mice. VBL induced both cell-cycle alteration and a highly significant (P less than 0.001) increase of the hyperploid cell frequency. On the basis of these and previous (Costa et al., 1988) observations it seems that the non-disjunctional activity of NTA in the mouse is confined to meiotic processes.

Nitrilotriacetic acid (NTA) does not induce chromosomal damage in mammalian cells either in vitro or in vivo

We used human lymphocyte cultures to repeat the experiments under the very particular conditions of nitrilotriacetic acid (NTA) treatments (high doses: up to 10(-2) M; very long exposure times: up to 5 days) which have been described as being able to induce chromosomal aberrations, and we also performed the more conventional treatments (24-48 h of exposure) as suggested in the protocols adopted by the EEC-OECD. Mitomycin C was routinely used as a positive clastogenic control. NTA did not significantly increase the frequency of chromosomal aberrations in any of the different experimental conditions adopted. Furthermore, no induction of micronuclei was observed in mouse polychromatic erythrocytes after treatment in vivo for up to 48 h with NTA (200-400 mg/kg b.w.), whereas the frequency of micronuclei was significantly increased by mitomycin C (1 mg/kg b.w.).

Nitrilotriacetic acid (NTA) induces aneuploidy in Drosophila and mouse germ-line cells

The ability of nitrilotriacetic acid (NTA) to induce aneuploidy was studied in the germ line of both Drosophila and the mouse. The Free Inverted X Chromosomes (FIX) genetic system, adopting a brooding scheme, was used to detect induced aneuploidy in Drosophila, and a cytogenetic method based on chromosomal counting in secondary spermatocytes was used in the mouse. In Drosophila a highly significant (P less than 0.001) increase of aneuploidies was produced by NTA (5 x 10(-2) M), which was greater than that produced by colchicine (7.5 x 10(-6) M) and 5-fluorodeoxyuridine (10(-4) M), which were used as positive controls. Brooding effects were observed with NTA, which produced a maximum induction of chromosomal gain in brood I, suggesting a possible stage-specific action during meiosis. The ability of NTA (275 mg/kg body weight) to induce meiotic aneuploidy (hyperhaploidy) also was confirmed in the mouse (P less than 0.001), where all the aneuploidies detected were attributable to treatment of the metaphase I stage.