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M D Shelby

Publications and source records attributed to M D Shelby.

At least 19 recordsLinked to original sources

Induction of micronucleated erythrocytes in rodents by diisopropylcarbodiimide and dicyclohexylcarbodiimide: dependence on exposure protocol.

The induction of micronucleated erythrocytes by diisopropylcarbodiimide (DIC) and dicyclohexylcarbodiimide (DCC) was investigated as part of a U.S. National Toxicology Program (NTP) evaluation of the subchronic toxicity of these chemicals. Analysis of peripheral blood smears from male and female B6C3F1 mice exposed to 17.5-140.0 mg DIC/kg/day by skin painting for 13 weeks revealed dose-related increases in the frequency of micronucleated normochromatic erythrocytes (MN-NCE) in both sexes. Results of a similar 13-week peripheral blood micronucleus (MN) test with DCC (1.5-12.0 mg/kg/day) were also positive, although the increases in MN-NCE were not as great as those observed with DIC. In contrast to the positive results of the subchronic skin-painting studies in mice, acute bone marrow MN studies with DIC and DCC in male F344 rats, using intraperitoneal (i.p.) injection, yielded negative results. Both the acute and the subchronic exposures included doses that produced clinical signs of toxicity. Acute mouse bone marrow MN tests with DIC administered in single or triple i.p. injection protocols were subsequently conducted to determine if the differing responses between mice and rats were due to species or protocol differences. The results of these acute tests were negative or equivocal. Because the subchronic studies produced positive results, it was hypothesized that these carbodiimides required multiple treatments over an extended period of time to produce an increase in MN-erythrocytes. To confirm the original response, a second dermal subchronic study was conducted with DIC; the protocol was modified to include sequential blood samplings to permit monitoring MN frequencies over time. The data demonstrated a small but consistent induction of micronucleated erythrocytes in mice treated with DIC by skin painting.

Administration, Cutaneous

Unlike other chemicals, etoposide (a topoisomerase-II inhibitor) produces peak mutagenicity in primary spermatocytes of the mouse.

The cancer chemotherapy agent, and topoisomerase-II inhibitor, etoposide (VP-16) produced both recessive mutations at specific loci and dominants at other loci with peak frequencies in primary spermatocytes, a cell type in which the topo-II gene has been shown to be activated. Etoposide thus differs from all other chemicals whose germ-cell-stage specificity has been analyzed. No effects of etoposide exposure of spermatogonial stem cells ( approximately 15, 000 offspring scored) were detectable by either mutagenicity or productivity endpoints. The significant mutagenic response that followed exposure of poststem-cell stages ( approximately 25,000 offspring scored) showed a clear peak, with three of four specific-locus mutants, and three of four dominant mutants conceived during weeks 4 or 5 (days 22-35) post-injection, a period that also encompassed the dominant-lethal peak. For this period, the induced specific-locus rate (with 95% confidence limits) at a weighted-average exposure of 75.1 mg etop/kg was 59.5 (14.6, 170. 9)x10-6/locus. At least 3 of the 4 specific-locus mutations were deletions, paralleling findings with etoposide or analogs in other test systems where a recombinational origin of the deletions has been suggested. Because, unlike other chemicals that induce deletions in male germ cells, etoposide is effective in stages normally associated with recombinational events, it will be of interest to determine whether this chemical can affect meiotic recombination.

Animals

Induction of mortality and malformation in Xenopus laevis embryos by water sources associated with field frog deformities.

Water samples from several ponds in Minnesota were evaluated for their capacity to induce malformations in embryos of Xenopus laevis. The FETAX assay was used to assess the occurrence of malformations following a 96-hr period of exposure to water samples. These studies were conducted following reports of high incidences of malformation in natural populations of frogs in Minnesota wetlands. The purpose of these studies was to determine if a biologically active agent(s) was present in the waters and could be detected using the FETAX assay. Water samples from ponds with high incidences of frog malformations (affected sites), along with water samples from ponds with unaffected frog populations (reference sites), were studied. Initial experiments clearly showed that water from affected sites induced mortality and malformation in Xenopus embryos, while water from reference sites had little or no effect. Induction of malformation was dose dependent and highly reproducible, both with stored samples and with samples taken at different times throughout the summer. The biological activity of the samples was reduced or eliminated when samples were passed through activated carbon. Limited evidence from these samples indicates that the causal factor(s) is not an infectious organism nor are ion concentrations or metals responsible for the effects observed. Results do indicate that the water matrix has a significant effect on the severity of toxicity. Based on the FETAX results and the occurrence of frog malformations observed in the field, these studies suggest that water in the affected sites contains one or more unknown agents that induce developmental abnormalities in Xenopus. These same factors may contribute to the increased incidence of malformation in native species.

Animals

Determination of tamoxifen and metabolites in serum by capillary electrophoresis using a nonaqueous buffer system.

Tamoxifen (TAM), an antiestrogen, is widely used to treat hormone-dependent breast cancer in post-menopausal women. TAM may be used as a chemopreventive agent in women of child-bearing age; however, few data exist describing potential TAM-induced fetal toxicity. In support of the National Toxicology Program's characterization of reproductive and developmental effects of TAM, this work describes an analytical technique utilizing capillary electrophoresis (CE) for the detection of circulating levels of TAM, N-desmethyltamoxifen (DMT), and 4-hydroxytamoxifen (4-HT) in maternal rodent serum. Greater than 90% of 3H-labeled TAM was extractable from serum using 98:2 hexane-isoamyl alcohol. Optimum separation of TAM, DMT, and 4-HT was obtained on a 57 cmx50 microm capillary using a nonaqueous buffer system of 1:1 methanol-acetonitrile containing 50 mM ammonium acetate and 1% acetic acid. 4-Dimethylaminopyridine was used as internal standard. Temperature and voltage were optimized at 40 degrees C and 15 kV, respectively. The limit of detection of TAM by UV detection at 214 nm was approximately 800 amol. TAM and DMT were confirmed in serum of female rats 4 h following a single oral dose of 120 mg/kg. Transplacental exposure of TAM to fetal tissue will be evaluated using this technique.

Animals

Mammalian germ cell mutagenicity of ENU, IPMS and MMS, chemicals selected for a transgenic mouse collaborative study.

A collaborative study to systematically assess transgenic mouse mutation assays as screens for germ cell mutagens has been conducted. Three male mouse germ cell mutagens (ENU, iPMS and MMS) were selected for testing. This paper provides a brief review of the effects reported for those 3 chemicals in the most commonly used non-transgenic germ cell mutagenicity assays, namely the dominant lethal, heritable translocation, and specific locus tests. Additionally, information on the DNA reactivity and the molecular nature of mutations induced by these chemicals is summarized.

Animals

Mutation assays in male germ cells from transgenic mice: overview of study and conclusions.

Three confirmed mouse germ cell mutagens, ethyl nitrosourea (ENU), isopropyl methanesulphonate (iPMS) and methyl methanesulphonate (MMS), have been evaluated for their activity as mutagens to the germ cell DNA of two strains of transgenic mice (lac I, Big Blue and LacZ, Muta Mouse). Both testicular DNA and epididymal sperm DNA were evaluated. A range of sampling times was studied, from 3 days post-dosing to 100 days post-dosing. ENU and iPMS were mutagenic to both testicular DNA and epididymal sperm DNA. Mutant frequencies were higher for both chemicals in DNA recovered from testicular tissue than in epididymal sperm DNA. Likewise, mutant frequencies were higher for both DNA samples at the later sampling times. MMS was not mutagenic under any condition of test. A good level of qualitative agreement in test results was seen for the two assays and for the same assays conducted in different laboratories. The level of quantitative agreement was not as high, but was, nonetheless, generally good. Recommendations for the future conduct of transgenic rodent germ cell mutation assays are made. The test data are discussed within the context of the larger question of how such assays should be integrated into the chemical hazard assessment process.

Animals

Multilaboratory comparison of in vitro tests for chromosome aberrations in CHO and CHL cells tested under the same protocols.

Different test results have been reported for the same chemicals in two in vitro chromosome aberration test systems, CHL cells tested by a Japanese protocol and CHO cells tested by the US National Toxicology Program [Sofuni et al., Mutat Res 241:173-213,1990]. Here, laboratories in Japan, the US and the UK tested 9 such chemicals in CHL and CHO cells using the same protocols and found all 9 positive in both cell types; differences in earlier conclusions with these chemicals were due mainly to test protocol, not to different sensitivities of the cells. The most important protocol difference is sampling time. Chemicals that were negative in the NTP series using a sampling time of 10 to 13 hours often produced positive results when retested here with a 20- to 24-hour sampling time. While positive results were obtained in both cell types, CHL cells sometimes had higher aberration levels and survived at higher doses than CHO cells would tolerate. This may reflect some intrinsic difference in sensitivity but may also be affected by factors such as cell cycle length and culture media (e.g., oxygen scavenging capacity). The collaboration reported here also contributed to a better understanding of scoring aberrations, especially "gaps"; there was good agreement on what types of aberrations should be included in the totals when scoring criteria were clearly defined, for example, many changes classified as "gaps" by the Japanese system were classified as "breaks" in the scoring systems used in the United States and the United Kingdom, and were appropriately included in total aberration counts.

Animals

Dominant lethal mutations, heritable translocations, and unscheduled DNA synthesis induced in male mouse germ cells by glycidamide, a metabolite of acrylamide.

The hypothesis that acrylamide induces dominant lethal mutations and heritable translocations in male mice, not through direct adduction, but by conversion to the reactive epoxide, glycidamide, was investigated. Three studies, namely, induction of dominant lethal mutations, heritable translocations, and unscheduled DNA synthesis in spermatids, which were conducted earlier in this laboratory for acrylamide, were also performed for glycidamide to determine its mutagenic properties and to compare responses. Results of these studies are consistent with the proposal that in vivo conversion to glycidamide is responsible for the mutagenicity of acrylamide in male mice.

Animals

Chlorambucil and bleomycin induce mutations in the specific-locus test in female mice.

Specific-locus studies have shown chlorambucil (CHL) and bleomycin (BLE) to be mutagenic in mouse oocytes, almost doubling the number of chemicals previously known to induce mutations in females. The overall CHL-induced mutation rate in oocytes is, however, one order of magnitude below that for male meiotic and postmeiotic stages, and only 1/50 that for early spermatids. For BLE, no specific-locus data for males are available for comparison, but the chemical had earlier been found negative for dominant-lethal induction in males. Both BLE and CHL were significantly mutagenic only in mature and maturing oocytes. In keeping with an earlier report, BLE produced a high incidence of dominant lethals in these stages. CHL failed to induce dominant lethals, indicating that for mature and maturing oocytes, in contrast with results for males, sensitivity to dominant-lethal mutations is not a prerequisite for induction of specific-locus mutations. Exposure of immature oocytes to either BLE or CHL produced neither dominant lethals nor significant induction of specific-locus mutations; however, CHL gave evidence of killing immature oocytes. By contrast, BLE, which has been considered a radiomimetic chemical, does not appear to kill immature oocytes and thus differs markedly from radiation exposures equivalent for dominant-lethal induction. Therefore, the failure to recover specific-locus mutations cannot be ascribed to cell selection resulting from oocyte killing, as has sometimes been done for radiation. Adding results on the nature of the CHL- and BLE-induced mutations to prior information, the estimated minimum proportion of large DNA lesions induced in oocytes by chemicals becomes 35.3%, significantly different from the corresponding figure (approximately 70%) for radiations. For chemical treatments, the oocyte proportion is highly significantly above the 3.6% induced in spermatogonia, but only on the borderline of statistically significant difference from that induced in postspermatogonial stages.

Animals

IPCS harmonization of methods for the prediction and quantification of human carcinogenic/mutagenic hazard, and for indicating the probable mechanism of action of carcinogens.

A flow chart is presented as a recommended sequence of tests to predict the carcinogenic hazard, and to predict and quantify the mutagenic hazard to germ cells of chemicals to humans. Ten associated principles of testing for these endpoints are also suggested. These recommendations are the result of a meeting convened under the auspices of the International Programme on Chemical Safety (IPCS), as part of their project on 'Harmonization of Approaches to the Assessment of Risk from Exposure to Chemicals'. The meeting was held at Carshalton, Surrey, from 13-17 February 1995.

Animals

Assessing environmental chemicals for estrogenicity using a combination of in vitro and in vivo assays.

Because of rampant concern that estrogenic chemicals in the environment may be adversely affecting the health of humans and wildlife, reliable methods for detecting and characterizing estrogenic chemicals are needed. It is important that general agreement be reached on which tests to use and that these tests then be applied to the testing of both man-made and naturally occurring chemicals. As a step toward developing a comprehensive approach to screening chemicals for estrogenic activity, three assays for detecting estrogenicity were conducted on 10 chemicals with known or suspected estrogenic activity. The assays were 1) competitive binding with the mouse uterine estrogen receptor, 2) transcriptional activation in HeLa cells transfected with plasmids containing an estrogen receptor and a response element, and 3) the uterotropic assay in mice. The chemicals studied were 17 beta-estradiol, diethylstilbestrol, tamoxifen, 4-hydroxytamoxifen, methoxychlor, the methoxychlor metabolite 2,2-bis(p-hydroxyphenyl)-1,1,1-trichloroethane (HPTE), endosulfan, nonylphenol, o,p'-DDT, and kepone. These studies were conducted to assess the utility of this three-assay combination in the routine screening of chemicals, or combinations of chemicals, for estrogenic activity. Results were consistent among the three assays with respect to what is known about the estrogenic activities of the chemicals tested and their requirements for metabolic activation. By providing information on three levels of hormonal activity (receptor binding, transcriptional activation, and an in vivo effect in an estrogen-responsive tissue), an informative profile of estrogenic activity is obtained with a reasonable investment of resources.

Animals

Study design and sample sizes for a lacI transgenic mouse mutation assay.

Design features that adjust and account for excess variation in a transgenic mouse mutation assay based on a lacI target transgene from E. coli are considered. These features include proper identification of plate, packaging reaction, and animal identifier codes throughout the experimental and analysis phases of the study, "blocking" of exposed and unexposed animals when preparing and plating multiple packaging reactions from the same genomic DNA sample, separating sectored mutant plaques and complete mutant plaques before performing any quantitative analyses, and testing for sources of excess variation attributable to features of the experimental protocol--such as plate-to-plate (within packaging reactions), packaging reaction-to-packaging reaction (within animals), and animal-to-animal (within study). Control and ethylnitrosourea-treated animal data are presented from a fully designed study in the lacI assay. The study design incorporates many of these experimental principles. Statistical methods to identify excess variability are noted, and the designed study data are used to illustrate the types of variability encountered in practice. A standard statistical test for two-sample testing is highlighted, from which recommendations are made for sample size selection in future studies.

Analysis of Variance

Comparison of results from mouse bone marrow chromosome aberration and micronucleus tests.

Tests for the induction of chromosomal aberrations (ABS) and micronuclei (MN) in bone marrow cells of mice have been conducted on 65 chemicals. Although these tests were not conducted with the purpose of comparing the outcomes of these two in vivo genetic toxicity endpoints, the availability of these test results permits such a comparison. Based on studies to date, results from the 2 tests agree for more than 80% of the chemicals; 17 gave positive results in both tests, and 36 gave negative results in both. Seven chemicals were positive only for ABS and 5 were positive only for MN. Three chemicals that were originally concluded to be positive for ABS but not for MN were found to induce MN when the MN protocol was modified to more closely reflect the ABS protocol. Among the 12 chemicals for which there are discrepant results, there are only 2 for which the difference is convincing. One of these, selenium sulfide (MN negative, ABS positive) remains an enigma; further studies are being conducted. The second, isoprene (MN positive, ABS negative) will be difficult to pursue because the studies reported here were done by inhalation exposure. Based on the outcomes of these comparisons, protocol factors, rather than endpoint specificity, appear to be the major source of discrepant test results. Thus, these results do not support a recommendation that both tests be conducted in a primary testing scheme for genetic toxicity.

Animals

Mutagenesis and human genetic disease: an introduction.

This special issue attempts to provide a fresh perspective on the importance of germ-cell mutagenesis studies and restate the questions and challenges inherent in efforts to minimize the incidence of human genetic diseases. We are working in a time when rapidly advancing molecular technologies provide the tools that permit a more detailed understanding of germ-cell mutagenesis and genetic disease. Meanwhile, discoveries of new genetic disease phenomena challenge our abilities to conceive and develop research models for their study. It is hoped that the collection of articles in this issue will serve to stimulate interest in scientists of varied disciplines and help focus those interests on the issues surrounding the relationship between environmental mutagens and human genetic disease.

Aneuploidy

Phenolphthalein: induction of micronucleated erythrocytes in mice.

Phenolphthalein was tested for the induction of micronucleated erythrocytes in mice. Results of an initial investigation revealed significant, dose-related increases in micronucleated polychromatic erythrocytes (MN-PCE) and normochromatic erythrocytes (MN-NCE) in peripheral blood samples of male and female mice exposed to 0.6% to 5% phenolphthalein (approximately 1100 to 10,000 mg/kg/day) in feed for 90 days (Dietz et al., 1992). Results from a second long-term feed study with Swiss CD-1 mice confirmed this effect. However, administration of comparable doses of phenolphthalein by corn oil gavage on two consecutive days gave negative results in a mouse bone marrow micronucleus test. Subsequent tests were performed to clarify the conflicting results seen in the chronic exposure, dosed-feed, peripheral blood studies and the acute, corn oil gavage, bone marrow studies. Phenolphthalein was administered to male B6C3F1 mice in feed (3%) for 14 days. Peripheral blood samples taken at 4, 7, and 14 days all showed significant increases in micronucleated PCE; bone marrow samples taken on days 7 and 14 also were clearly positive for micronucleus induction. Therefore, comparable results were obtainable from both bone marrow and peripheral blood analyses. Because of the negative results in the two-exposure gavage test, additional tests were then designed to investigate the effects of bolus vs continuous dosing, feeding vs gavage administration, and corn oil vs feed as a carrier for phenolphthalein. Results of these tests indicated that the rate of exposure to phenolphthalein affects the frequency of induced MN-PCE and that micronucleated erythrocytes can be induced by phenolphthalein either by feeding or by corn oil gavage administration. In all the acute exposure studies, relatively high doses of phenolphthalein (2000-6000 mg/kg/day for at least 2 days) were required to induce micronuclei. The positive results obtained with phenolphthalein in vivo were consistent with the results of an in vitro chromosomal aberration test in Chinese hamster ovary cells, where dose-related increases in aberrations were noted only in cells treated in the presence of induced rat liver S9.

Animals

Dominant lethal and heritable translocation tests with chlorambucil and melphalan in male mice.

Chemicals used in the treatment of cancer include several that are potent mutagens in a range of in vitro and in vivo assays. For some, genetic effects have also been demonstrated in humans, detected as chromosomal aberrations in peripheral lymphocytes. Because (1) many of these agents are confirmed mutagens, (2) humans are exposed to them in relatively high doses, and (3) an increasing number of early cancer victims are surviving to reproductive age, it is important that information be available on the genetic and reproductive hazards associated with exposure to these agents. Chlorambucil and melphalan are structurally related chemicals that are included in our efforts to identify and assess such hazards among cancer chemotherapy agents. To date, both have been reported to induce specific locus mutations in germ cells of male mice (Russell et al., 1989; Russel et al., 1992b) and melphalan is one of very few chemicals shown to induce such mutations in spermatogonial stem cells. More recently, both chemicals were found to have strong reproductive effects in female mice (Bishop and Generoso, 1995, in preparation). In the present studies, these chemicals were tested for the induction of dominant lethal mutations and heritable translocations in male mice. Both chemicals were found to have reproductive effects attributable to cytotoxicity in specific male germ cell stages and to induce dominant lethal mutations and heritable translocations in postmeiotic germ cells, particularly in mid to early stage spermatids. Thus, relatively extensive data are now available for assessing the genetic and reproductive hazards that may result from therapeutic exposures to these chemicals.

Animals