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Toxicologic studies of N-trichloromethylthio-4-cyclohexene-1,2-dicarboximide (captan): its metabolism by rat liver drug-metabolizing enzyme system.

The degree of toxicity caused in rats by captan (N-trichloromethylthio-4-cyclohexene-1,2-dicarboximide) administered intraperitoneally is greater than that induced by orally administered captan. With regard to its effect on the drug-metabolizing enzymes of rat liver, the activity of aniline hydroxylase and the level of cytochrome P-450 were found to decrease in the treated rats 24 h after a single oral dose (650 mg/kg). The loss was even greater in the animals receiving diethyl maleate 1 h prior to captan. Furthermore, usual increase in the activity of drug biotransformation enzymes seen after phenobarbital treatment appears to decrease in rats dosed with this funaicide. In vitro incubations of rat liver microsomes with captan resulted in a profound loss of cytochrome P-450 and the acitivty of benzphetamine N-demethylase as well as aniline hydroxylase. Although the inhibition of drug-metabolizing enzyme activity by captan was observed in microsomal incubations with or without NADPH, a detectable amount of carbonyl sulfide (COS) was found only in the incubations that contained captan plus NADPH. Carbonyl sulfide appears to arise from a captan-derived metabolite, thiophosgene (CSCl2), which decomposes to COS in aqueous solutions and in the presence of NADPH inhibits the activity of drug biotransformation enzymes.

Aniline Hydroxylase↗

Transgenic strains of the nematode C. elegans in biomonitoring and toxicology: effects of captan and related compounds on the stress response.

The fungicide, captan, induces a cellular stress response in the soil nematode Caenorhabditis elegans. Transgenic C, elegans, which produce beta-galactosidase as a surrogate stress protein, reveal that captan-induced stress is localized mainly to muscle cells of the pharynx. The stress response is elicited by captan concentrations above 5 ppm and occurs within five hours of the initial exposure to the fungicide. Higher concentrations of captan, up to the solubility limit, increase the intensity of the response. Adult nematodes are significantly more sensitive to captan than are larvae. Captan also inhibits feeding in C. elegans, and nematodes exposed to captan rapidly cease muscular contractions in the pharynx. Stress induction and feeding inhibition are also caused by the related fungicides, captafol and folpet, but not by the parent compounds, phthalimide and tetrahydrophthalimide. The inhibition of feeding caused by compounds which elicit the cellular stress response may be an important survival mechanism for C, elegans.

Animals↗

Differential effects of captan on DNA polymerase and ribonuclease H activities of avian myeloblastosis virus reverse transcriptase.

Captan was used as an inhibitor of avian myeloblastosis virus reverse transcriptase to study the polymerase and RNase H catalytic activities. With purified enzyme, RNase H activity was 10-fold more sensitive to captan than was either the DNA-dependent or RNA-dependent DNA polymerase activity. Inhibition of the RNA-dependent polymerase activity could be prevented by dTTP. Conversely, inhibition of this polymerase activity was enhanced by template/primer. The calculated KdTTP of the uninhibited reaction was 5.6 microM. Kinetic studies allow for the proposition of a model for the interaction of captan with the polymerase active center. RNase H activity showed a sigmoidal relationship between activity and substrate concentration. Nuclease activity decreased in Vmax with no change in the Hill coefficient in the presence of captan. Addition of dithiothreitol to the incubation cocktail prevented inhibition by captan of both RNA-dependent polymerase and RNase H activities, suggesting that the (trichloromethyl)thio moiety of captan is involved in the inhibitory action. Captan inhibition suggests the presence of essential amino residues in both polymerase and RNase H active centers.

Avian Leukosis Virus↗

GC-ITMS determination and degradation of captan during winemaking.

Captan and its metabolite tetrahydrophthalimide (THPI) were determined in grapes, must, and wine by GC-ITMS. Pesticides were extracted with acetone/petroleum ether (50:50 v/v). Because of the high selectivity of the ITMS detector, no interferent was found and cleanup was not necessary. Recoveries from fortified grapes, must, and wines ranged between 90 and 113% with a maximum coefficient of variation of 11%. Limits of quantitation were 0.01 mg/kg for both compounds. In model systems, captan and its metabolites, THPI, cis-4-cyclohexene-1,2-dicarboxylic acid, and 1,2,3,6-tetrahydrophthalamic acid, were determined by HPLC. The degradation of captan during winemaking was studied. Captan degraded in must, giving 100% THPI, and at the end of fermentation, only THPI was found in wine. The degradation of captan to THPI was due to the acidity in must and wine. This metabolite was present at low levels on grapes, and, unlike captan, it had no negative effect on the fermentative process. Model systems showed that the mechanism of disappearance of captan in grapes was due to photodegradation and codistillation.

Captan↗

Analysis of captan on nitrile glove surfaces using a portable attenuated total reflection fourier transform infrared spectrometer.

This study developed a method to produce uniform captan surface films on a disposable nitrile glove for quantitation with a portable attenuated total reflection Fourier transform infrared (ATR-FTIR) spectrometer. A permeation test was performed using aqueous captan formulation. Uniform captan surface films were produced using solvent casting with 2-propanol and a 25 mm filter holder connected to a vacuum manifold to control solvent evaporation. The coefficient of variation of the reflectance at 1735 +/- 5 cm(-1) was minimized by selection of the optimum solvent volume, airflow rate, and evaporation time. At room temperature, the lower to upper quantifiable limits were 0.31-20.7 microg/cm2 (r = 0.9967; p < or = 0.05) for the outer glove surface and 0.55-17.5 microg/cm2 (r = 0.9409; p < or = 0.05) for the inner surface. Relative humidity and temperature did not affect the uncoated gloves at the wavelength of captan analysis. Glove screening using ATR-FTIR was necessary as a control for between-glove variation. Captan permeation, after 8 hours exposure to an aqueous concentration of 217 mg/mL of Captan 50-WP, was detected at 0.8 +/- 0.3 microg/cm2 on the inner glove surface. ATR-FTIR can detect captan permeation and can determine the protectiveness of this glove in the field.

Algorithms↗

Lack of induction of nuclear aberrations by captan in mouse duodenum.

The fungicide, captan, is known to induce point mutations in vitro. In extremely high doses, technical grade captan leads to duodenal tumors in mice. In short-term in vivo assays for genotoxicity, equivocal results have been obtained with captan. In this study, the genotoxicity of captan was studied in vivo in the proximal small intestine of the mouse, the site of its oncogenicity. Orally administered captan up to 4,000 mg/kg body weight failed to induce a response in the small intestine nuclear aberration assay in a wide range of doses under a variety of experimental conditions, including pretreatment of animals with L-buthionine-S, R-sulfoximine (an inhibitor of glutathione biosynthesis). 1,2,3,6-Tetrahydrophthalimide and bis (trichloromethyl)disulfide, two compounds that have been identified as impurities in technical grade captan, also failed to produce positive results in this assay.

Animals↗

Evaluation of toxic potential of captan: Induction of hsp70 and tissue damage in transgenic Drosophila melanogaster (hsp70-lacZ) Bg9.

The study investigated the working hypothesis that a widely used fungicide captan exerts toxic effects on nontarget organisms. Transgenic Drosophila melanogaster (hsp70-lacZ) was used as a model by assaying stress gene expression as an endpoint for cytotoxicity and also to evaluate whether stress gene expression is sufficient enough to protect and to prevent tissue damage against toxic insult of the chemical. The study was further extended to understand the effect of the pesticide on development, life cycle, and reproduction of the organism and finally to evaluate a concentration of the chemical to be nontoxic to the organism. The study showed that (i) captan causes cytotoxicity at and above 0.015 ppm; (ii) at 0.0015 ppm captan, absence of hsp70 expression in the exposed organism was evaluated as the concentration referred to as no observed adverse effect level (NOAEL) for Drosophila; (iii) emergence pattern of flies was affected only at the highest concentration of captan by 4 days, while hatching and survivorship were unaffected even at this concentration; (iv) reproductive performance was significantly affected only at 125.0 and 1250.0 ppm captan, while in the lower dietary concentrations no such deleterious effects were observed; (v) at 1250.0 ppm, hsp70 failed to protect the cells from toxicant assault after 48 h exposure, thus leading to tissue damage as revealed by Trypan Blue staining. The present study shows the cytotoxic potential of captan and further reveals the application of stress genes in determining NOAEL and its expression as bioindicator of exposure to environmental contaminants.

Animals↗

Captan alters transcription in Escherichia coli permeabilized by toluene.

RNA synthesis was measured in toluenized E. coli by the incorporation of radiolabeled precursor into either acid precipitable or phenol extracted RNA. Exposure to captan (100 microM) caused a 2.6 fold increase in the apparent rate of RNA synthesis. When captan was tested for its effect on the initiation of RNA synthesis, using either rifampicin-treated cells or by measuring the incorporation of gamma [32P]ATP or gamma [32P]GTP, no change was observed in the number of RNA chains being initiated. Thus, captan does not exert its influence at the level of initiation of nascent chains. However, captan did have an effect on chain growth. From calculations of the incorporation of precursors molecules, RNAs isolated from treated cells were measured to be an average of 2.7 times longer than those from untreated cells. RNA chain lengths were also analyzed by polyacrylamide gel electrophoresis. By this latter technique it was also shown that cells exposed to captan synthesized RNAs that were longer than those of untreated cells. Alterations in the degradation of RNA molecules do not account for the captan mediated response in RNA synthesis.

Adenosine Triphosphate↗

The bacteriostatic action of captan: alterations of RNA metabolism in E. coli.

The growth of E. coli in broth cultures was inhibited in a concentration dependent manner by the addition of captan. Treated cells showed no evidence of lysis and maintained a viable character. Following a single exposure to 500 microM captan, cells exhibited a lag period of approximately six hr and then grew to maximum density. During the period of arrested growth, captan apparently inhibited the synthesis of RNA as measured by the incorporation of tritiated uridine into acid-insoluble material. This apparent inhibition was due in part to a captan mediated decrease in the uptake of uridine from the media into the soluble nucleotide pool. By means of RNA isolation, polyacrylamide gel electrophoresis, and RNA quantitation, it was demonstrated that captan caused a selective loss of large (16 and 23 S) ribosomal RNA's. However, cellular concentrations of transfer RNA and 5S ribosomal RNA were unaffected by captan treatment.

Captan↗

Initiation of transcription in nuclei is inhibited by captan.

Captan (N-trichloromethylthio-4-cyclohexene-1,2-dicarboximide) was examined for its effects on bovine liver nuclear RNA synthesis. Transcription was measured by [3H] UTP incorporation into either acid insoluble product or isolated RNA. Captan (1 mM) was found to inhibit RNA synthesis 50% in intact nuclei and 70% in a hypotonic lysate of nuclei. Individual RNA polymerase activities were distinguished in both intact nuclei and hypotonic lysate by alpha-amanitin sensitivity. Captan inhibited RNA polymerase I and II activities to an equal extent in both intact and lysate systems. The sulfhydryl compound dithiothreitol (DTT) protected the RNA polymerase activities from inhibition by captan. Initiation of transcription in intact nuclei was measured by [gamma-32P] ATP incorporation into purified RNA and was found to be inhibited 75% by 1 mM captan. This report describes the inhibition of nuclear RNA polymerase activities by captan and suggests a possible mechanism for its toxic effect on eukaryotic polymerases.

Amanitins↗

Induction of gastric mucosal cell proliferation by the fungicide captan: role of tyrosine kinases.

Captan (1,2,3,6-tetrahydro-N-trichloromethylthiophthalmide), a widely used fungicide, has been shown to induce carcinoma in the gastrointestinal tract of rodents. However, little is known about the captan induction of early biochemical changes in the gastrointestinal tract. The present investigation examines the changes in gastric mucosal proliferative activity in 2-month-old Fischer 344 rats following a daily injection (s.c.) of captan (100 mg/kg body wt.) in DMSO while being infused (osmotic minipump) with the same compound (7.14 mg captan/kg body wt./h) for 2 weeks. The control rats received the vehicle the same way. The change in proliferative activity was related to tyrosine kinase (Tyr-k) activity and tyrosine-specific phosphorylation of protein(s) in gastric mucosal membranes since these intracellular events are thought to play an important role in proliferation, differentiation and transformation of cells. After 2 weeks of captan administration gastric mucosal DNA synthesis and thymidine kinase activity (indicators of proliferative activity) were increased by 330% (P less than 0.025) and 98% (P less than 0.025), respectively, when compared with the corresponding controls. Gastric mucosal DNA content was also increased by 90% (P less than 0.025) after administration of captan. These increases were associated with about 3-fold rise in Tyr-k activity and 2-fold increase in tyrosine phosphorylation of 6 mucosal membrane proteins with Mr of 105, 90, 60, 55, 48 and 37 kDa. We conclude that captan stimulates gastric mucosal cell proliferation, and activation of Tyr-k and tyrosine phosphorylation of certain membrane proteins may be important in the regulation of this process.

Animals↗

Optical biosensor for simultaneous detection of captan and organophosphorus compounds.

The optical biosensor consisting of GST and acetylcholinesterase (AChE)-immobilized gel film was developed to detect captan and organophosphorus compounds simultaneously in contaminated water. The sensing scheme was based on the measurement of decrease of products formation (s-(2,4-dinitrobenzene) glutathione and alpha-naphthol by GST and AChE, respectively) due to the inhibition by captan and organophosphorus compounds. The absorbance of s-(2,4-dinitrobenzene) glutathione and alpha-naphthol was detected at 400 and 500 nm, respectively, by a proposed optical biosensor system. It was observed that AChE was inhibited by both captan and organophosphorus compounds, and GST was inhibited only by captan. The simultaneous detection and quantification of captan and organophosphorus compounds could be successfully achieved by the proposed sensor system. The proposed biosensor could successfully detect the captan and organophosphorus compounds concentration from 0 to 2 ppm.

Acetylcholinesterase↗

Effect of captan on DNA synthesis in the liver and testes of rats.

Rats were fed a diet containing 0.3% (w/w) captan for 2, 4 and 12 weeks and compared with controls, and with rats fed 0.02% (w/w) N-2-acetylaminofluorene (AAF). Cell loss was evaluated from the drop of previously [14C] labeled DNA and DNA synthesis was expressed as fractional incorporation of [3H] dThd into hepatic and testicular DNA. The feeding of AAF for 12 weeks produced in the liver a cell loss and a stimulation of DNA synthesis (+ 348%); in the testes, a cell loss but an inhibition of DNA synthesis (- 84%) occurred. The continuous feeding of captan produced no cytotoxic effect on the liver but increased hepatic DNA synthesis between 2 and 4 weeks of diet (+ 100%). Then, the synthesis induction seemed to reach a plateau until 12 weeks. The captan diet did not provoke any cytotoxic effect on testes until 4 weeks of feeding. At 12 weeks, some loss of testicular DNA and of [14C] labeling indicated a toxic effect of captan. The testicular DNA synthesis was clearly inhibited by captan diet at 4 weeks (- 22%), and the inhibition increased at 12 weeks (- 27%). Experiments done at a higher level of captan (1.5% in the diet) showed that the effect on DNA synthesis in liver and testes was dose-related.

2-Acetylaminofluorene↗

Protective effect of glutathione on the in vitro inhibition of hepatic cytochrome P-450 by captan.

The in vitro effect of various concentrations of captan on hepatic microsomal cytochrome P-450 from pehnobarbital-pretreated rats was studied. The I-50 value, namely the concentration of the inhibitor necessary to produce 50% loss of cytochrome P-450 was determined from theplotted inhibition curve. The presence of ethylenediaminetetraacetic acid (EDTA) in microsomal incubations prior to the addition of captan failed to prevent the loss of cytochrome P-450 by captan. In contrast, reduced glutathione (0.5 mM) added to microsomal incubations before captan (0.1 mM) afforded almost complete protection of cytochrome P-450 from captan inhibition. These data indicate that the inhibitory effect of captan on vitally important drug-metabolizing enzyme system, of which cytochrome P-450 is a major component, can be prevented by prior presence of reduced glutathione (GSH) but not of EDTA.

Animals↗

Residues of captan and folpet in strawberries and grapes.

Fresh strawberries and grapes grown in Michigan and Indiana were surveyed for residues of captan and folpet, 2 fungicides commonly used on these crops. The fungicides were reportedly applied to the crops by overhead irrigation, tractor sprayer, or aerial spraying, in amounts ranging from 0.5 to 6 lb formulation/acre for captan and from 1 to 4 lb formulation/acre for folpet. Reported dates of last application ranged from just 2 days to nearly 5 months before samples were collected. Twenty-eight strawberry samples and 24 grape samples were collected of crops field-treated with one or both of these fungicides. Samples were analyzed by previously described methodology. Captan residues were found in all strawberry samples, ranging from less than 0.01 to 1.5 ppm. Folpet was found in only one strawberry sample at 0.041 ppm. Captan residues were found in only 6 grape samples, ranging from less than 0.01 to 0.082 ppm. Folpet residues were found in 12 grape samples, ranging from less than 0.01 to 0.50 ppm. All residues were well below the current tolerances of 25 ppm for both captan and folpet in strawberries and 50 ppm for captan and 25 ppm for folpet in grapes. Residue levels of these surface-applied, nonsystemic fungicides were inconsistent with amounts and dates of application, most likely because of variations in weather conditions, especially rainfall. Residues were quite stable in frozen sample homogenates, declining only 5-10% after 2 months.

Captan↗

Captan and fenitrothion dissipation in field-treated cauliflowers and effect of household processing.

Field trial studies have been performed with captan and fenitrothion on cauliflower to propose maximum residue limits and to study the dissipation of the pesticides. Residue levels have been determined at different times following good laboratory practice using gas chromatography with mass spectrometric detection. The behaviour of residue levels of these compounds after household processing has been analysed using gas chromatography with electron capture detection. Seven days after treatment, residue levels of captan could be detected, but not of fenitrothion. The half-lives of dissipation for captan and fenitrothion were calculated as 0.9 and 1.8 days respectively. Washing did not significantly affect the residual amounts of captan and fenitrothion observed in raw vegetables; however, after cooking, captan had degraded completely, whereas residue levels of fenitrothion were not modified significantly.

Brassica↗

Determination of tetrahydrophtalimide and 2-thiothiazolidine-4-carboxylic acid, urinary metabolites of the fungicide captan, in rats and humans.

Capillary gas chromatographic (GC) methods using sulphur and mass selective detection for the qualitative and quantitative determination of tetrahydrophtalimide (THPI) and 2-thiothiazolidine-4-carboxylic acid (TTCA), urinary metabolites of the fungicide captan in rat and humans, were developed. Urinary detection limits were 2.7 micrograms/l for THPI and 110 micrograms/l for TTCA. Intraperitoneal and oral administration of captan to rats resulted in a 48-h cumulative urinary excretion of THPI of 1%-2% and 3%-9% of the dose, respectively. Cumulative urinary excretion of TTCA over 48 h ranged from 2% to 5% of the captan dose for the respective routes of administration. In urine of non-exposed human subjects, neither THPI nor TTCA could be detected. In urine of fruit-growers who were occupationally exposed to captan, both THPI and TTCA could be detected. Based on these results, THPI and TTCA are proposed as promising parameters for the biological monitoring of occupational exposure to captan.

Agriculture↗

Interaction of glutathione transferase P1-1 with captan and captafol.

Glutathione transferase (GST, EC 2.5.1.18) P1-1 was strongly inhibited by captan and captafol in a time- and concentration-dependent manner. The IC50 values for captan and captafol were 5.8 microM and 1.5 microM, respectively. Time-course inactivation of GSTP1-1 by two pesticides was prevented by 3 microM of hexyl-glutathione, but not by methylglutathione. The fact that the inactivated enzyme recovered all the 5,5'-dithiobis(2-nitrobenzoic acid) titrable thiol groups, with concomitant recovery of all its original activity after treatment with 100 microM dithiothreitol, suggested that captan and captafol were able to induce the formation of disulfide bonds. That the inactivation of GSTP1-1 by captan and captafol involves the formation of disulfide bonds between the four cysteinil groups of the enzymes was confirmed by the SDS-PAGE experiments on nondenaturant conditions. In fact, on SDS-PAGE, GSTP1-1 as well as the cys47ala, cys101ala, and cys47ala/cys101ala GSTP1-1 mutants treated with captan and captafol showed several extra bands, with apparent molecular masses higher and lower than the molecular mass of native GSTP1-1 (23.5 kDa), indicating that both intra- and inter-subunit disulfide bonds were formed. These extra bands returned to the native 23.5 kDa band with concomitant restoration of activity when treated with dithiothreitol.

Captan↗