Biomedical subjects
Publications and source records attributed to R Valencia.
Twenty-two chemicals were tested for mutagenicity in the sex-linked recessive lethal (SLRL) mutation assay after being fed to Drosophila melanogaster larvae. One compound, maleic hydrazide, was found to be mutagenic. It was tested for the ability to produce reciprocal translocations (RTs) and was positive in that assay as well.
U-48753E is a potential human drug which was subjected to a battery of short-term assays for genetic activity. The compound was negative in the Salmonella (Ames) test, the in vitro UDS assay, the mouse bone-marrow micronucleus test and the Drosophila sex-linked recessive lethal assay. However, it was weakly positive in the CHO/HPRT assay in the presence of metabolic activation (S9). The weak positive response might easily have been labeled artifactual since there was no dose response and the dose level producing positive findings varied from experiment to experiment. In addition, the weak positive response was not confirmed in V79 cells. However, a reproducible dose-related increase in mutants was observed in the AS52/XPRT assay in the presence of S9. Metabolism of this drug proceeds through conversion of aliphatic N-methyl groups to formaldehyde. Addition of formaldehyde dehydrogenase to the S9 resulted in elimination of the mutagenicity of the compound in AS52 cells. Thus, the mutants were probably induced by formaldehyde. From the endogenous levels of formaldehyde in human blood, and the limiting potential therapeutic dose levels, the genotoxic hazard associated with U-48753E is marginal. This assessment of risk and its quantitation depend upon an understanding metabolism and exposure limits imposed by known side effects of the drug. This study can serve as a model for quantitative genetic risk assessment when mutagenicity is due to N-demethylation and formation of formaldehyde in situ.
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The genotoxic effects of methyl isocyanate (MIC) were investigated using four short-term tests: the Salmonella reversion assay (Ames test), the Drosophila sex-linked recessive lethal assay, and the sister chromatid exchange (SCE) and chromosomal aberration assays in cultured Chinese hamster ovary (CHO) cells. No evidence was found for the induction of mutations in either Salmonella or Drosophila. MIC did, however, induce SCEs and chromosomal aberrations in CHO cells both in the presence and absence of Aroclor-induced rat liver S-9.
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Separation of the major bases of DNA along with seven minor methylated ones was obtained by reversed-phase high-performance liquid chromatography using an isocratic elution system. Application of this procedure to DNA treated in vitro by N-methyl-N-nitrosourea has allowed identification of two induced minor bases; a third one was resolved using a slightly modified mobile phase. Baseline resolution of 3-methyl- and 5-methylcytosine, detected in Euglena DNA hydrolyzates, was also achieved.
Results are presented from mutagenesis testing in Drosophila of 20 coded compounds. Two compounds were positive in the sex-linked recessive lethal test, and two were inconclusive. The positive compounds were calcium chromate in adult feeding experiments and ferrocene after adult injection. The two inconclusive compounds were 2,4-diaminophenol dihydrochloride and hexachlorocyclopentadiene. Compounds that produced a positive response were assayed for chromosome breakage using the conventional translocation test. Calcium chromate was negative in the translocation test, and ferrocene was positive. Many of the test compounds were poorly soluble in water, raising questions regarding the effective concentration to which the flies were exposed.
Forty-eight chemicals were tested for mutagenicity in Drosophila melanogaster. Each compound was tested first for the induction of sex-linked recessive lethals (SLRLs) by feeding the chemical in a solution of 5% aqueous sucrose. If it was not mutagenic by this route, the chemical was tested by injection in a solution of 0.7% aqueous NaCl. If found inactive, the compound was not tested further. If it was mutagenic, the compound was tested for the induction of reciprocal translocations (RTs) using the exposure protocol and germ cell stage that yielded positive results in the SLRL assay. Eight chemicals (diglycidylresorcinol ether, AF-2, alloxan monohydrate, 1-aziridine ethanol, p,p'-DDE, dichloroacetonitrile, 1,3-dichloropropene, and 3,3'-dimethylbenzidine dihydrochloride) were found to induce SLRLs. Only diglycidylresorcinol ether also induced RTs.
Results from Drosophila mutagenicity tests of 45 chemical compounds assayed for the National Toxicology Program are presented. Nine compounds were judged positive and four equivocal in the sex-linked recessive lethal test. The nine positive compounds were acetin, allyl glycidyl ether, cyclophosphamide, 1,2-dibromo-3-chloropropane, 2,3-dibromo-1-propanol, dimethylcarbamyl chloride, 1,2-epoxy-butane, lasiocarpine, and N-nitrosopiperidine. The results for chloral hydrate, maleic hydrazide, propantheline bromide, and trifluralin were equivocal. Of the nine compounds positive in recessive lethal induction, only two--allyl glycidyl ether and dimethylcarbamyl chloride--failed to induce translocations. The remaining 32 were judged to be nonmutagenic under the conditions used.
Spontaneous sex-linked recessive lethal mutation frequencies may vary with time. Examination of approximately 1.7 X 10(6) Drosophila melanogaster X chromosomes in three laboratories suggests two sources of variation in the spontaneous mutation frequency. First, the underlying mutation rate may change with time, suggesting genetic drift among the genes controlling the spontaneous mutation rate. In one set of experiments, the recessive lethal frequency increased from 0.2% to 0.4% in 6 years. Second, there may be seasonal variation in the mutation frequency even under apparently controlled conditions, suggesting that uncontrolled environmental factors may play an important role in determining the mutation frequency. Therefore, concurrent controls should be used in mutation experiments except in cases in which the frequency in the untreated control is so low as to be unmeasurable in a single experiment or the control frequency can be shown not to vary with time.
Fifty-three chemicals were tested for mutagenicity in Drosophila melanogaster by adult feeding and, where results were negative, by adult injection for the induction of sex-linked recessive lethal mutations in meiotic and postmeiotic germ cell stages of Canton-S males. One compound was tested by inhalation. Those compounds that induced lethal mutations were tested further for the induction of reciprocal translocations. Seventeen of the 53 compounds (acetaldehyde, 2-aminoanthracene, bromoform, t-butyl hydroperoxide, chlorambucil, trans-cinnamaldehyde, crotonaldehyde, 1,3-dichloro-5,5-dimethylhydantoin, 3,4-dichloronitrobenzene, dimethoxane, 2,4-dinitrotoluene, 1,2-epoxy-3,3,3-trichloropropane, formaldehyde, furfural, halothane, HC yellow 4, and picric acid) were found to induce lethal mutations and three (2-aminoanthracene, chlorambucil,and crotonaldehyde) also induced reciprocal translocations.
The mutagenicity of fifteen insecticides, five fungicides, four herbicides, and an acaricide commonly used in Pakistan was evaluated by employing thirteen short-term bioassays. The genetic endpoints used included point or gene mutation, primary DNA damage, and chromosomal effects. Initially, all pesticides were tested in a "core" battery of four in vitro bioassays. A carefully selected group among these chemicals was retested in higher level test systems to confirm the results obtained in the initial phase. Of the pesticides tested, only a small portion consistently displayed mutagenicity across test systems. The Saccharomyces cerevisiae bioassays detected mutagenicity for the largest number of pesticides. The Salmonellaces typhimurium strain, TA100, was able to detect genetic activity in all of the pesticides that produced positive results in this bioassay. The cytogenetic effects observed from the Vicia faba root assay were consistent with those obtained in mammalian cells in culture. All pesticides which displayed mutagenicity were not carcinogenic in animal bioassays but, in general, mutagenicity in a battery of short-term bioassays was a reliable indicator of the carcinogenic potential in animals. A simple test battery is proposed for evaluating the genetic potential of agricultural pesticides.
As part of the validation phase of the Drosophila melanogaster segment of the National Toxicology Program, a comparison has been made of positive and negative controls for sex-linked recessive lethal mutations and reciprocal translocations from three laboratories. This comparison involves approximately 700,000 spontaneous recessive lethal mutation tests, 70,000 spontaneous translocation tests, and screens for genetic damage induced by N-nitrosodimethylamine and beta-propiolactone. Spontaneous frequencies for lethal mutations and translocations were homogeneous in the laboratories regardless of solvent or broods sampled. Inhomogeneity was observed in induced frequencies among laboratories, but the variation was no greater than that found within a laboratory.
The mutagenic potential of diethylene glycol monobutyl ether (diEGBE) was examined with a Tier I battery of in vitro assays followed by a Tier II in vivo Drosophila sex-linked recessive lethal assay. The in vitro battery consisted of: the Salmonella mutagenicity test, the L5178Y mouse lymphoma test, a cytogenetics assay using Chinese hamster ovary cells and the unscheduled DNA synthesis (UDS) assay in rat hepatocytes. Results of the Salmonella mutagenicity test, the cytogenetics test, and the rat hepatocyte assay were negative at concentrations up to 20 microL/plate, 7.92 microL/mL, and 4.4 microL/mL, respectively. Toxicity was clearly demonstrated at all high doses. A weak, but dose-related increase in the mutation frequency (4-fold increase over the solvent control at 5.6 microL/mL with 12% survival) was obtained in the L5178Y lymphoma test in the absence of metabolic activation. Results of the mouse lymphoma assay were negative in the presence of the S-9 activation system. The significance of the mouse lymphoma assay were negative in the presence of the S-9 activation system. The significance of the mouse lymphoma assay results were assessed by performing the Tier II sex-linked recessive lethal assay in Drosophila in which the target tissue is maturing germinal cells. Both feeding (11,000 ppm for 3 days) and injection (0.3 microL of approximately 14,000 ppm solution) routes of administration were employed in the Drosophila assay. Approximately 11,000 individual crosses with an equal number of negative controls were performed for each route of administration. diEGBE produced no increase in recessive lethals under these conditions.(ABSTRACT TRUNCATED AT 250 WORDS)
The term 'chromosome mutations' was chosen and defined for this review to refer to alterations of chromosome structure (reciprocal, heritable translocations), of chromosome number (loss or gain of a whole chromosome), or of chromosome content (loss or gain of a part of a chromosome). Chromosome mutations may result from chromosome breakage (clastogenesis) and its consequences or from disruption of chromosome behavior during cell division (nondisjunction). State-of-the-art protocols are outlined to test for heritable translocations, for whole-or partial chromosome loss (clastogenesis), and for whole chromosome loss or gain (nondisjunction). The literature up to 1980 was reviewed and 106 papers were selected for the evaluation of 116 chemicals for one or more chromosome mutation end points. The criteria used for acceptance of data from the literature were not stringent, as most of this work was done some time ago and for purposes other than testing. The main criterion was that germ cell stage sampling was correct. For the evaluation of the accepted data, numerical requirements were set up, using as a guide the control data from all the papers. Compounds were classified, when possible, as mutagenic (+) or nonmutagenic (-). Those not classifiable, usually due to insufficient numbers of chromosomes tested, were listed as inconclusive (inc). Of 61 compounds tested for heritable translocations, 27 were positive, 8 were negative, and 26 were inconclusive. Of the 35 with conclusive data, only 21 also have definitive carcinogenesis classifications (all positive). Of these, 19 were deemed mutagenic, which gives agreement of 90.5%. Of the 76 compounds tested for clastogenesis by the chromosome loss test, 26 were positive, 13 were negative, and 37 were inconclusive. Of the 39 with conclusive data, only 20 also have definitive carcinogenesis classifications. 15 of the 19 carcinogens were positive. Four of the carcinogens were negative and 1 noncarcinogen was positive, for an overall agreement of 75%. Of 44 compounds tested for nondisjunction, 15 were positive, 13 were negative, 16 were inconclusive. Of the 28 compounds with conclusive data, only 9 have definitive carcinogenesis classifications (all positive). Five of these were deemed negative and agreement was only 44%. It should be noted that these data do not fairly represent these short-term tests as conducted with current protocols. A more equitable comparison could be achieved with planned experiments that include the sex-linked recessive lethal (SLRL) test in the comparison.
The test for sex-linked recessive lethals (SLRL) in Drosophila melanogaster has been used to detect induced mutations since 1927. The advantage of the test for both screening and hazard evaluation is its objectivity in testing for transmissible mutations in the germ cells of a eukaryote. Statistical criteria for both positive and negative mutagenicity at the highest concentration tested under a particular exposure condition were developed by the Work Group, and a recommended protocol for future testing was agreed upon. For 421 compounds there were sufficient data available in the literature for analysis; 198 compounds were found to be positive and 46 negative at the highest concentration tested. Most experiments had been done for objectives of pure research rather than for deliberately screening for mutagenicity, although many of the 421 chemicals were selected for testing because of suspected mutagenicity. Therefore, the statement of 198 positive and 46 negative should not be taken as an example of the proportion of mutagens in the environment. In three sets of experiments with D. melanogaster that were done specifically for screening, one involving 40 compounds for the Environmental Protection Agency (EPA), the others involving 13 for the Food and Drug Administration (FDA), only 6 mutagens were discovered. After completion of the classification of compounds according to their response in the SLRL test, the compounds were classified as to their carcinogenic response according to the list of Griesemer and Cueto (1980). There were 62 compounds that could be classified as positive or negative for both carcinogenesis and mutagenesis. Of the 62 compounds, there was agreement between the carcinogenesis and mutagenesis classification in 56 (50 positive and 6 negative), or 90% would have been correctly classified as to carcinogenesis from only the SLRL test. Because of inadequate sample size, 177 compounds could not be classified as positive or negative according to the statistical criteria established by the Work Group. This large number of inadequately tested compounds reflects the fact that many of the experiments were not done for screening. Further work is needed on the compounds with inadequate sample size.(ABSTRACT TRUNCATED AT 400 WORDS)
Kathon biocide, an aqueous solution containing a mixture of 5-chloro-2-methyl-4-isothiazolin-3-one and 2-methyl-4-isothiazolin-3-one in an approximate ratio of 3:1, was tested for mutagenic activity in Salmonella typhimurium, L5178Y mouse lymphoma cells in culture and Drosophila melanogaster. Tests also were conducted for chromosome aberrations in vivo on mouse bone marrow cells, for DNA damage/repair in primary rat hepatocytes in culture, and for morphological transformation in C3H 10T1/2 cells in culture. Kathon biocide produced point mutations in the absence of a rat-liver metabolizing system in bacteria (strain TA 100) and mammalian cells in culture. In the presence of rat-liver metabolizing system a 10-fold higher concentration was required to induce point mutations in mammalian cells in culture. No mutagenic activity was observed with the metabolizing system and S. typhimurium. Negative results were obtained in the sex-linked recessive lethal assay in Drosophila, the in vivo cytogenetic assay in mice, the unscheduled DNA synthesis assay in cultured rat hepatocytes, and the in vitro cell transformation assay.
I trust that I have accomplished my aim in this presentation, to demonstrate that Drosophila mutagenesis testing protocols are varied and are adaptable. The choices are many, at different levels. First, the route of administration can be chosen that is most appropriate for the chemical compound or to duplicate the human exposure route or to obtain data needed for some particular purpose, such as comparative mutagenesis. Second, the genetic test scheme or combination of schemes can be chosen to suit the purpose of the testing (screening, risk evaluation, or comparative mutagenesis). Third, by treating the appropriate fly development stage and managing the mating and brooding procedures, the germ cell stage can be sampled that is the critical one for the mutagenic effect of that compound and the correct one for the end point to be observed. Fourth, in screening, using the SLRL assay, the experiment size can be adjusted in accordance with the test sensitivity desired, the projected use of the data, and time and cost restrictions. In summary, Drosophila melanogaster has long been known as a most versatile organism for genetic studies of all kinds--and we now know that this versatility extends to the evaluation of chemical compounds for mutagenic effects. If it were only a mammal!