Gene/Protein Disease Symptom Drug Enzyme Compound
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Query: UNIPROT:P56851 (epididymal)
 11,273 document(s) hit in 31,850,051 MEDLINE articles (0.00 seconds)

We are developing a data base that will allow us to select endpoints that would be useful in the detection of reproductive toxicity in a multigenerational test. In this effort, carbendazim (MBC), a known reproductive toxicant, was administered to male and female rats from weaning, through puberty, gestation, and lactation. A similar study was conducted with hamsters. In rats, MBC was administered at 0, 50, 100, 200, or 400 mg/kg/day. Hamsters were dosed at 0 or 400 mg/kg/day. In the parent (P0) generation, landmarks of puberty were measured. In females, estrous cyclicity, litter size, the number of implants, organ weights, and histology were assessed. Our assessment of the male rat included organ weights, testicular and epididymal sperm counts, a quantitative measure of sperm motility, sperm morphology, testicular histology, and endocrine measures. The growth, viability, and reproductive function of the offspring (F1) were observed during a 4-month period of continuous breeding. In the P0 of both species. MBC did not alter pubertal development, growth, or viability. The reproductive potential of the rats treated with MBC at 200 and 400 mg/kg/day was reduced due to effects on sperm production and fetal viability. In the male rat, MBC treatment markedly altered sperm morphology, testicular and epididymal weights, and sperm numbers and testicular histology. Fertility, sperm motility, and hormonal levels were altered, primarily in the males with very low sperm counts. The ability to conceive did not appear to involve a female factor. In P0 female rats, MBC administration caused postimplantation losses in the high-dosage groups and a few malformed rat pups were found in the litters from the 100 and 200 treatment groups. MBC was less toxic to the hamster than the rat. The only reproductive effects induced by MBC treatment were on sperm measures. Fertility of the P0 generation and fetal and neonatal (F1) viability were not decreased by MBC administration. In the male rat, testis weight, sperm numbers in the cauda epididymis and testis and sperm morphology were sensitive to the effects of MBC. In females, counting implantation scars at necropsy was useful, as this information allowed us to confirm pregnancy and identify postimplantation losses induced by MBC administration.
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PMID:Carbendazim-induced alterations of reproductive development and function in the rat and hamster. 222 56

This paper compares the statistical precision and biological sensitivity of multiple indices of reproductive function to infertility in the male rodent. The studies discussed include those that examined reproductive function in the male following perinatal exposure to reproductive toxicants and others in which the compounds were administered to young-adult males, often with very diverse results. For example, some chemicals that alter sex differentiation reduce fertility by affecting breeding performance alone (polychlorinated biphenyls (PCBs), fenarimol, or losulazine), without altering sperm and testicular measures. Others also markedly alter sex differentiation of the genitalia, the accessory glands and the testis in addition to their effects on central nervous system (CNS) sex differentiation and mating behavior (testosterone, flutamide, cyproterone acetate, tamoxifen, estradiol and diethylstilbestrol (DES)). In contrast, prenatal exposure to compounds that alter primary germ cell survival (busulphan, congo red) induce partial gonadal/germ cell agenesis without altering sex differentiation. These chemicals dramatically reduce testicular sperm production in the male offspring, and the most severely affected males are infertile. In a series of studies conducted in our laboratory, young male rats were exposed to known reproductive toxicants in a dose related manner from puberty, through young adulthood and breeding. We have found that the profile of effects varies considerably depending upon the chemical's mechanism of toxicity. When a compound produced infertility through direct effects of testicular function (Carbendazim (MBC) and dibutyl phthalate (DBP)), then testis weight, testicular histology, and testicular sperm head counts provided sensitive indicators of toxicity. In general, dramatic reductions in sperm production are required to induce infertility and these changes were accompanied by elevated serum luteinizing hormone (LH) and follicle-stimulating hormone (FSH) and changes in human chorionic gonadotropin (hCG)-stimulated testosterone synthesis. Chemicals that have hormonal activity, alter the internal endocrine environment, or directly effect CNS function induce a completely different profile of effects. For example, estrogen administration alters the function of the seminal vesicle and the endocrine system, and reduces epididymal sperm reserves; while testicular measures are relatively unaffected. Since very different spectrums of effects are produced by different compounds, no single endpoint will consistently be the most sensitive indicator of reproductive toxicity.(ABSTRACT TRUNCATED AT 400 WORDS)
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PMID:Correlation of sperm and endocrine measures with reproductive success in rodents. 266 89

Most effects of thyroid hormones appear to be mediated by the binding of triiodothyronine (T3) to nuclear triiodothyronine binding sites (NT3BS). Although thyroid hormones influence adipocyte metabolism, NT3BS have not been described in mature adipocytes yet. This report describes T3 nuclear binding in isolated nuclei from rat epididymal fat pad adipocytes. Nuclei were isolated by exposing collagenase-dispersed adipocytes to STM (sucrose, 0.25 mol/L; TRIS, 20 mmol/L; MgCl2, 1.1 mmol/L, pH 7.85) containing 0.5% (vol/vol) Triton X-100. Incubation of nuclei suspended in STM/EDTA (2 mmol/L)/DTT (5 mmol/L) with 125I-T3 and varying concentrations of unlabeled T3 at 37 degrees C for one hour revealed the presence of high-affinity, low-capacity NT3BS. Their MBC was 0.39 +/- 0.04 (SD) ng of T3 per milligram of DNA and their Kd was 1.4 +/- 0.5 (SD) X 10(-10) mol/L T3. Specific binding reached a plateau between 30 minutes and two hours of incubation. The addition of 5 X 10(-7) mol/L T3 to nuclei incubated for one hour with 2 X 10(-11) mol/L T3 completely displaced the specifically bound 125I-T3 within 30 minutes. Thyroxine (T4) and 3, 3', 5'-triiodothyronine (rT3) could displace 125I-T3 from the NT3BS but were less than 10% and 1% as effective, respectively, as T3. Rat epididymal fat pad adipocytes contain NT3BS, the binding characteristics of which are similar to those of rat hepatic NT3BS.
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PMID:Nuclear triiodothyronine binding sites in rat adipocytes. 632 15

Benomyl, a systemic fungicide, was administered to male Sprague-Dawley rats during the prepuberal, pubertal, or postpubertal stage of reproductive development. Animals received 5 or 10 daily treatments of 0, 125, 200, 250, 500, or 1000 mg benomyl/kg . d by gavage. Observations were made at selected intervals after exposure and included hematological parameters, body weight, tissue weights, total epididymal sperm counts, vas deferens sperm concentration, serum follicle-stimulating hormone ( sFSH ) levels, and testicular histology. Data presented here suggest that there is an age-related difference in sensitivity to benomyl. Animals that received benomyl treatments during prepuberty showed no significant treatment effects in tissue weights, total epididymal sperm counts, vas deferens sperm concentration, or sFSH . Animals that received at least 250 mg/kg . d during puberty or postpuberty showed one or more of the following effects: decreased testicular or epididymal weights, decreased epididymal sperm count, decreased vas deferens sperm concentrations, and/or testicular lesions. Histological examination of testicular tissue indicated a higher incidence of diffuse hypospermatocytogenesis in pubertal (20% of the treated animals) and postpubertal (40% of the treated animals) animals that were exposed to benomyl. These values were compared with those of the treated prepubertal animals, which had a 10% incidence of diffuse hypospermatocytogenesis , and with all of the control animals, which had no occurrences of this testicular lesion.
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PMID:Effect of benomyl on the reproductive development of male rats. 642 9

Benomyl is a benzimidazole fungicide that has been widely used on a variety of food crops and ornamental plants. It is known to cause adverse effects on reproductive systems, including decreased testicular and epididymal weights and reduced epididymal sperm counts and fertility. The brain aromatase gene is up-regulated by estrogens and estrogen mimics and considered a target gene to screen estrogen mimics. This study was designed to test the estrogenic potential and toxic effects of benomyl in the zebrafish system, and validated this system as a model that may correspond to the effect of benomyl in rodents. Concentrations of 20 x 10(-6), 40 x 10(-6) and 80 x 10(-6) M of benomyl-treated embryos showed decreased survival, hatching and heart rates, and increased incidence of malformations, such as pericardial edema, spinal lordosis, elongated heart, head edema, eye lens protrusion and caudal fin disappearance. Benomyl induced enhanced green fluorescent protein (EGFP) expression in the mediobasal hypothalamus (MBH) in transient zebrafish embryos with a brain aromatase-based reporter gene. In this study, we determined that benomyl has estrogenic potential based on zebrafish brain aromatase gene induction, and that benomyl is toxic at 20 x 10(-6) M concentration and higher. These results demonstrate the usefulness of zebrafish embryos as an in vivo system to examine the estrogenic and developmental toxic potential of unknown compounds.
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PMID:Benomyl induction of brain aromatase and toxic effects in the zebrafish embryo. 1905 95