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Oral toxicity of ferric dimethyl-dithiocarbamate (ferbam) and tetramethylthiuram disulfide (thiram) in rodents.

Single oral doses of ferbam, thiram, zineb, or maneb produced central nervous system stimulation followed by depression and alopecia. Ferbam and thiram were more toxic on the basis of weight than zineb; maneb was relatively nontoxic. There was no species difference in acute toxicity between rats and mice. In 13- and 80-wk feeding studies, the toxic effects of ferbam and thiram in rats were similar; however, thiram was more toxic on the basis of weight than ferbam. During the 80-wk feeding study, weight gain was reduced in ferbam-treated rats starting at daily doses of 8 mg/kg in males and 37 mg/kg in females and in thiram-treated rats staring at daily doses of 5 mg/kg in males and 26 mg/kg in females. Food consumption was reduced in proportion to the reduced weight gain. Death occurred in males fed 109 or 331 mg/kg.d ferbam and in males fed 58 or 132 mg/kg.d thiram. Female rats fed 96 mg/kg.d ferbam or 67 mg/kg.d thiram developed alopecia and ataxia, which led to paralysis of the hind limbs. Male rats fed ferbam or thiram had a more severe incidence of squamous metaplasia in the thyroid and fatty infiltration in the pancreas than control males. Ferbam or thiram reduced the incidence of spontaneous nephritis in both males and females. The male rats that were fed 109 or 331 mg/kg.d ferbam and died betweeen 1 and 5 wk had golden pigment in the reticuloendothelial cells of the spleen and in the enlarged mesenteric lymph nodes, associated with hemosiderosis. Moderate tubular degeneration of the testes with atypical spermatids in the epididymis occured in some rats fed 132 mg/kg.d thiram for 13 wk but not in rats fed up to 52 mg/kg.d for 80 wk. Periodic hematologic examination and terminal clinical blood tests did not reveal any severe changes. Ferbam and thiram did not alter the occurrence or latent period of the spontaneous tumors seen in control rats.

Animal Feed↗

Characterization of pregnancy outcome following thiram-induced ovulatory delay in the female rat.

A single injection of the dithiocarbamate fungicide, thiram, suppresses the proestrous surge of LH and delays ovulation for 24 h. In this study, we examined fertility after a thiram-induced delayed ovulation. Females were injected with thiram (50 mg/kg, IP) on proestrus (1300 h) and mated on the following evening. Control and thiram-treated, but nondelayed, females were injected and mated on the same day. The number of females in the thiram-delayed group that became pregnant was reduced and litter size on GD 20 was reduced: however, no obvious morphological anomalies were seen. The number of pregnant females and litter size was not altered in the thiram-nondelayed rats, indicating that it is the thiram-induced delay in ovulation and not the exposure to thiram per se that was responsible for altered pregnancy outcome. On GD 7 and 11, the number of live fetuses per litter was reduced in the delayed females, but the number of implantation sites was not different from controls. On GD 11 the mean developmental score, head length, crown-rump length, and somite number in the delayed group were also reduced, indicating retarded development of live embryos. These results demonstrate that delayed ovulation induced by a single thiram exposure does not alter the number of oocytes released or the number that implant. However, the concept from these females are compromised during midgestation.

Animals↗

Metabolism of a dithiocarbamate fungicide thiram to carbon disulfide in the rat and its hepatotoxic implications.

Thiram, tetramethylthiuram disulfide, is used extensively as an agricultural fungicide whose toxicity is largely dependent on its metabolism. The following experiments were carried out to investigate whether carbon disulfide (CS2) is a metabolic product of microsomal monooxygenase catalyzed metabolism of thiram in rats. Adult male Sprague-Dawley rats (160-200 g) were given thiram (60 mg/kg, b.wt.) in corn oil by intraperitoneal injection and placed individually in a metabolic apparatus. Concentration of CS2 in the breath was determined by drawing the expired air through a series of traps containing a CS2 complexing agent. Expiration of CS2 was almost complete within 5 hrs following thiram administration. The formation of CS2 from thiram was increased by pretreatment of rats with phenobarbital and decreased by SKF 525-A. Furthermore, measurement of the activities of hepatic microsomal and serum enzymes at 5 hrs and 24 hrs following thiram treatment indicated that thiram caused significant loss of cytochrome P-450 and benzphetamine N-demethylase activity only at 24 hrs interval whereas there was significant elevation of sorbitol dehydrogenase (SDH) and serum glutamic oxalacetic transaminase (SGOT) activity at 5 and 24 hrs after treatment. The data confirm that CS2 is an in vivo metabolite of thiram and may be, in part, responsible for the observed hepatotoxicity.

Animals↗

Carcinogenic and co-carcinogenic studies of thiram on mouse skin.

Thiram (tetramethyl thiuram disulfide), a carbamate fungicide, is used in the rubber processing industry as an accelerator and vulcanizing agent. Previous studies evaluated the tumorigenic potential of thiram in rodents, but failed to provide conclusive results. In the present study the tumorigenic potential of thiram was evaluated in Swiss albino mice by a two-stage initiation-promotion protocol and a long-term in vivo bioassay for carcinogenicity. Results revealed that following tumour initiation with thiram and promotion with 12-O-tetradecanoyl phorbol 13-acetate, skin tumours developed, mostly at the site of treatment (dorsal skin) in single and multiple dose-initiated animals. Similarly, papillomatous growths were observed on the dorsal skin of the mice initiated with a single subcarcinogenic dose of dimethylbenzanthracene and promoted with thiram. Thiram failed to provoke tumorigenesis when tested as a complete carcinogen for up to 52 wk and thereafter the study was terminated due to increased mortality. It is concluded that thiram has both tumour initiating and tumour-promoting potential in both sexes of Swiss albino mice following topical exposure at the tested dose level.

Administration, Topical↗

The dithiocarbamate fungicide thiram disrupts the hormonal control of ovulation in the female rat.

Thiram has been reported to inhibit dopamine-beta-hydroxylase (D beta H), thereby affecting norepinephrine (NE) synthesis. Because NE is a neurotransmitter that is known to play an important role in the hypothalamic regulation of pituitary function, the acute effects of the thiram on the hormonal control of ovulation in the rat were investigated. Ovariectomized, estrogen-primed female rats were given a single injection of thiram (0, 6, 12, 25, 50, and 100 mg/kg, i.p.) at 1100 h and serum LH was measured in serial bleeds. Thiram at 100 and 50 mg/kg completely blocked the LH surge in all rats tested, while 12 and 25 mg/kg blocked the surge in 40 and 75% of the treated animals, respectively. Six mg/kg had no effect. Ovulation was then assessed in intact, proestrous females in response to thiram administration (0, 12, 25, or 50 mg/kg) at 0900, 1100, 1300, or 1800 h. Ovulation was blocked by 25 and 50 mg/kg at 1300 h in all rats, but when injected at 1100 h only the 50 mg/kg dose was effective. No such blockade was found with 50 mg/kg injected at 0900 and 1800 h. To assess the influence of thiram on the LH surge in intact rats, additional females were dosed at 1300 h on the day of proestrus and blood collected over that same day. Thiram at 50 mg/kg blocked the LH surge in all rats, while 25 mg/kg blocked the surge in 60% of the females tested. No effect occurred with 12 mg/kg.(ABSTRACT TRUNCATED AT 250 WORDS)

Animals↗

Thiram and dimethyldithiocarbamic acid interconversion in Saccharomyces cerevisiae: a possible metabolic pathway under the control of the glutathione redox cycle.

A rapid decrease of intracellular glutathione (GSH) was observed when exponentially growing cells of Saccharomyces cerevisiae were treated with sublethal concentrations of either dimethyldithiocarbamic acid or thiram [bis(dimethylthiocarbamoyl) disulfide]. The underlying mechanism of this effect possibly involves the intracellular oxidation of dimethyldithiocarbamate anions to thiram, which in turn oxidizes GSH. Overall, a linear relationship was found between thiram concentrations up to 21 microM and production of oxidized GSH (GSSG). Cytochrome c can serve as the final electron acceptor for dimethyldithiocarbamate reoxidation, and it was demonstrated in vitro that NADPH handles the final electron transfer from GSSG to the fungicide by glutathione reductase. These cycling reactions induce transient alterations in the intracellular redox state of several electron carriers and interfere with the respiration of the yeast. Thiram and dimethyldithiocarbamic acid also inactivate yeast glutathione reductase when the fungicide is present within the cells as the disulfide. Hence, whenever the GSH regeneration rate falls below its oxidation rate, the GSH:GSSG molar ratio drops from 45 to 1. Inhibition of glutathione reductase may be responsible for the saturation kinetics observed in rates of thiram elimination and uptake by the yeast. The data suggest also a leading role for the GSH redox cycle in the control of thiram and dimethyldithiocarbamic acid fungitoxicity. Possible pathways for the handling of thiram and dimethyldithiocarbamic acid by yeast are considered with respect to the physiological status, the GSH content, and the activity of glutathione reductase of the cells.

Cytochrome c Group↗

Dietary no-effect level of a dithiocarbamate fungicide, thiram, evaluated from measurement data on rats. I. Choice of the model of the dose-response relationship.

Rats were fed diets containing various amounts of added thiram, a dithiocarbamate fungicide. As thiram feeding resulted in decreased appetite, control rats not receiving thiram were pair-fed to the experimental ones. On d 30 of the experiment the animals were weighed and sacrificed, and the following organs were weighed: liver, kidneys, heart, epididymal and perirenal fat pads, testes, seminal vesicles, tibia, adrenals, and thyroid. Liver concentrations of lactate, pyruvate, beta-hydroxybutyrate, acetoacetate, ATP, and ADP were determined by enzymatic-spectrofluorimetric assay. For each parameter studied and each thiram dosage, values for treated rats were compared to those for control rats and the probability under the null hypothesis was computed. These probabilities were transformed into probits, logits, or "Weibull transforms" and plotted against the logarithms of the respective doses. Models were fitted to the data by linear regression techniques. Finally, the dose inducing the least significant difference (LSD dose), and the dose considered "safe" at P = 0.95, 0.99, and 0.999 were calculated. Significant pesticide-induced changes in the following parameters were found: food intake; weights of the whole body, kidneys, epididymal and perirenal fat pads, testes, and seminal vesicles; and liver beta-hydroxybutyrate/acetoacetate and lactate/pyruvate ratios. As the models did not differ in fit to the experimental data or in computed LSD doses, they were discriminated on the grounds of their underlying theoretical assumptions and their prediction of safe doses in a long-term study. The log-probit model was rejected for the former reason, and it was shown that the Weibull model foresees a nonnegligible risk of change, with thiram feeding at low doses, for too many parameters. The analysis resulted in the selection of the log-probit model for further use. Weight of fatty tissues was the most sensitive parameter and, using the log-probit model, the predicted no-effect dose at the 95 percent confidence level was 38 ppm thiram in the diet.

Animals↗

Comparative effects of two dithiocarbamates disulfiram and thiram, on adrenal catecholamine content and on plasma dopamine-beta-hydroxylase activity.

Both disulfiram (tetraethylthiuram disulfide), an alcohol aversive drug, and thiram (tetramethyl-thiuram disulfide), a widely used pesticide, significantly increased the dopamine pool in the adrenal glands of dosed rats. The dopamine increase was detectable within 4 h of oral dosing with 100 mg/kg of either dithiocarbamate and peaked 24 h later at 10 times control values. In control rats the dopamine turnover was 0.51 h-1 as calculated by the assumed first order decline of dopamine after a single injection of alpha-methyl-p-tyrosine (alpha-MT, 400 mg/kg i.p.) resulting in a dopamine-beta-hydroxylase (DBH) activity of 0.73 nmol/h per pair of adrenals. In the adrenals of rats pretreated with thiram and then injected with alpha-MT, the adrenal dopamine content did not significantly decline, indicating that thiram reduced the conversion of dopamine to noradrenaline, eventually leading to the observed dopamine increase. Plasma DBH activity was significantly reduced 4 h and 24 h after dosing with thiram, but was unchanged after treatment with disulfiram. The determination of plasma DBH activity could be a marker to monitor the effect of thiram on catecholamine metabolism in occupationally exposed workers but not that of disulfiram in abstinent alcoholics.

Administration, Oral↗

An example of interaction between environmental pollutants: modification of thiram toxicity to freshwater organisms by nitrites or nitrates in relation to nitrosamine synthesis.

Thiram, a dithiocarbamate fungicide, is known to evolve to dimethylnitrosamine (DMNA) when associated with nitrites. Conditions of appearance of that carcinogenic compound have been studied in short-term experiments by association of the fungicide, nitrates or nitrites, and species representative of freshwater biota. DMNA has been estimated by GLC equipped with a specific detector. Chlorella vulgaris can rapidly produce nitrites from nitrates and DMNA is obtained in presence of thiram. Daphnia magna can also synthesize DMNA but nitrites have to be added to the medium. Increased toxicity of thiram is observed. The same results are obtained on Cyprinus carpio and for a part on Brachydanio rerio. When the species are associated in a 15-day experimental food chain, and intoxicated algae feed the two other levels, no significant transfer is observed. Nevertheless, some DMNA hazard may exist for particular species exposed to thiram associated with nitrites or even nitrates if algae are present.

Animals↗

Mutagenic activity of thiram in Ames tester strains of Salmonella typhimurium.

The mutagenic activity of thiram was investigated in 4 histidine-requiring strains of Salmonella typhimurium (TA1535, TA100, TA1538, TA98) with and without activation by liver microsomes. In strains TA1535 and TA100, thiram induces mutations without metabolic activation. The presence of rat-liver microsome fraction, cysteine or glutathione abolish its mutagenic activity in these strains. In contrast, thiram requires metabolic activation for the expression of its mutagenic activity in TA1538 and TA98 strains. The compounds containing the sulphydryl group abolish mutagenic activity of thiram in these strains, too.

Drug Evaluation, Preclinical↗

The effect of thiram on the germ cells of male mice.

The effects of thiram or tetramethylthiuram disulphide on the germ cells of Swiss albino male mice were evaluated by analysing spermatocytes (derived from treated spermatogonia) for chromosomal aberrations and by the sperm-head morphology assay. The total doses tested were 80, 200 and 320 mg/kg body weight given by gavage in three consecutive daily doses, the top dose being slightly below the LD50 of thiram. There was a significant increase in the frequency of numerical chromosomal aberrations and abnormal sperms in mice treated with thiram at all dose levels. Such results could have implications for man in that they suggest that undue exposure to thiram could result in the birth of human infants with numerical chromosomal aberrations.

Animals↗

Potential effects of Thiram on Medicago - R. meliloti symbiotic association.

The effects of Thiram and 2 commercial Thiram formulations on the growth and respiration of rhizobia were tested to compare the extent of bacteriostasis under controlled conditions. Although bacteriostasis was measurable at all concentrations tested, liquid cultures grew to maximum optical density in Thiram suspensions containing less than 10 micrograms/ml. Percentage germination, root elongation, and subsequent nodulation by R. meliloti of 2 cultivars of alfalfa, were determined in thiram suspensions to determine potential physiological effects of the fungicide on the host plant. Conditions were identified which produced enhancement or inhibition of germination, root elongation and development of nodular nitrogenase activity. At concentrations of the fungicide recommended for seed application, only minor, temporary bacteriostasis was observed as a possible negative effect while germination rates of fungi-contaminated seed were markedly increased.

Dose-Response Relationship, Drug↗

Induction of tumors of the nasal cavity in rats by concurrent feeding of thiram and sodium nitrite.

Simultaneous feeding to rats of thiram with sodium nitrite was carried out to assess the possibility of formation of carcinogenic N-nitroso derivatives in vivo. Following the administration of feed containing 500 ppm thiram plus 2000 ppm sodium nitrite for 104 w, a high incidence of tumors of the nasal cavity was found in both sexes, 18 of 24 males and 15 of 24 females. No nasal-cavity tumors were seen in untreated rats, or those given 500 ppm of thiram or 2000 ppm of sodium nitrite alone. A 20% incidence of papillomas of the forestomach was also seen in the rats of both sexes given the combined treatment. The other significant difference in incidence of tumors between the rats given thiram with or without nitrite was a decreased number of animals with monocytic leukemia, which is a common neoplasm in untreated F344 rats.

Animals↗

No evidence of effect on male mice germ cells after acute treatment with thiram.

Thiram is a dithiocarbamate compound widely used for industrial processes and agriculture. Animal studies reveal that this compound may affect the male reproductive system. Aim of this study was to test, using sensitive testicular parameters, whether thiram directly affects germinal cells. For this purpose, B6C3F1 mice were intraperitoneally injected with thiram in oil (single dose: 75 mg/kg; repeated five daily doses: 25 mg/kg). Although both treatments were toxic, none of the parameters examined, i.e., testis weight, spermatid head number, specific enzyme levels at different times after treatment (14, 28, 35, 56 days) showed significant variations from the controls. On the contrary, in the positive controls (treated with chlorambucil), a marked reduction of sperm head number as well as a decrease of lactate dehydrogenasex and sorbitol dehydrogenase activity levels were evidenced at day 28, with a tendency to recover at day 35. Under these conditions thiram did not cause cytotoxicity on differentiating spermatogonia and on late spermatocyte stages of mice gonads.

Animals↗

Alterations in hepatic biochemistry of mice intoxicated with MIC, carbaryl and thiram.

The effect of different doses of methyl isocyanate (MIC), carbaryl and thiram on liver microsomal mixed-function oxygenases (MFO) was studied in adult Swiss Portan mice by intraperitoneal (i.p.) injection for different durations. The LD50 dose of all three toxicants after 0.75 h of administration could increase cytochrome P-450 and cytochrome b5 contents (82-143%), and the 1/4 LD50 of these compounds could elicit the same effect after 168 h (168-393%). The 1/4 LD50 dose of thiram decreased the cytochrome P-450 content below the control level (69.62%) in 0.75 h and the same dose of MIC could decrease the cytochrome P-450 level by 40% compared to the control after 3 days of consecutive injection. The activities of drug-metabolizing enzymes (aminopyrine demethylase--NADH and NADPH-linked--and aniline hydroxylase) were found to increase with all three compounds in general. Marked changes in the activity of the marker enzyme glucose-6-phosphatase were also seen after i.p. injection if MIC, carbaryl and thiram. These findings suggested that these compounds were hepatotoxic, which could be due to their carbamylating nature.

Aminopyrine N-Demethylase↗

Further in vitro and in vivo mutagenicity assays with thiram and ziram fungicides: bacterial reversion assays and mouse micronucleus test.

The fungicides thiram and ziram have been assayed in a battery of nine bacterial strains of different genetic specificity. The results obtained suggest the induction of excisable DNA lesion(s), and indicate similar mutability of strains with AT or GC base pairs at target sites. This mutagenic profile is clearly distinct from that of oxidative mutagens, and it does not support the proposed role of oxidative stress in the mechanism of dithiocarbamates mutagenicity in bacteria. Furthermore, the bone marrow micronucleus test has been carried out in B6C3F1 mice with intraperitoneal administration of high grade thiram (12.5-50 mg/kg) and ziram samples (2.5-10 mg/kg in males, and 5-20 mg/kg in females). Thiram produced a significant increase of micronucleated PCEs in male mice sampled 48 h after treatment with 25, 37.5, and 50 mg/kg. No significant increase was detected in treated females. Ziram, tested in a lower range of doses because of its higher toxicity, resulted negative in both sexes. Both the acute toxicity and the ratio polychromatic/normochromatic erythrocytes indicated some sex specificity in the toxic effects induced by these dithiocarbamates in the B6C3F1 mouse.

Animals↗

Clastogenic effects of the dithiocarbamate fungicides thiram and ziram in Chinese hamster cell lines cultured in vitro.

We report here the results obtained using the dithiocarbamate fungicides thiram and ziram to investigate the induction of chromosomal aberrations (CAs) in Chinese hamster ovary (CHO) cells both in the absence and presence of S9 metabolism, and in a Chinese hamster epithelial liver (CHEL) cells which retain metabolic competence to activate different classes of promutagens/procarcinogens. Both thiram and ziram proved to be strong chromosome breaking agents in the CHEL cells and CHO cells in the presence of S9 metabolism. These findings suggest that thiram and ziram require metabolic conversion to become genetically active, and corroborate the evidence that CHEL cells are suitable to activate and detect a broad spectrum of chemical procarcinogens including these two pesticides.

Animals↗

Analysis of dithiocarbamate fungicides. Reaction products of the thiuram disulphide fungicide thiram (TMTD) during acid hydrolysis.

The acid hydrolysis products (CS2, COS, and H2S) of thiram (tetramethylthiram disulphide, TMTD) absorbed in a methanolic amine reagent (ethylenediamine, piperidine) were investigated by second derivative UV spectroscopy. When the hydrolysis temperatures are below the boiling point the formation of the side products COS and H2S at the expense of CS2 is unavoidable. Failure to carefully scrub the liberated gases with a lead acetate solution leads to the absorption of H2S also in the amine reagent and, like COS, causes an absorption at 230 nm that is erroneously attributed to COS. With the second-derivative technique it has been undoubtedly proved that, under the conditions of the Deutsche Forschungsgemeinschaft method S 15, thiram liberates CS2 and COS in a molar ratio of 1.92 to 0.06 (average of eight determinations) but not in a molar ratio of 1.5 to 0.5, as previously reported by some workers. Under these conditions it is impossible, contrary to earlier claims, to differentiate thiram from other dithiocarbamates based on the ratio of the hydrolysis products in residue analysis.

Hydrogen-Ion Concentration↗