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Biomedical subjects

R E Chapin

Publications and source records attributed to R E Chapin.

At least 55 records · Page 3Linked to original sources

Mechanism of the testicular toxicity of boric acid in rats: in vivo and in vitro studies.

High-dose boric acid (BA) exposure produces testicular lesions in adult rats characterized by inhibited spermiation (IS) that may progress to atrophy. In vivo and in vitro studies addressed possible mechanisms. In vivo, boron tissue disposition was examined, since no detailed data existed, and relevant boron concentrations for in vitro studies needed to be set. Since BA induces riboflavinuria and also affects calcium/phosphorus homeostasis, and testis zinc appears essential for normal testis function, we examined BA effects on flavin status and testis levels of phosphorus (P), calcium (Ca) and zinc (Zn). Data showed that the testicular toxicity and central nervous system (CNS) hormonal effect were not due to selective boron accumulation in testis or brain/hypothalamus, with testis boron concentrations at approximately 1 to 2 mM; that riboflavin deficiency is not involved, due to both the absence of overt signs of deficiency and effects on tissue flavin content during BA exposure; and that changes in testis P, Ca and Zn levels did not precede atrophy, and are therefore unlikely to be mechanistically relevant. In vitro studies addressed the hallmarks of the BA testicular toxicity: the mild hormone effect, the initial IS, and atrophy. No effect of BA on the steroidogenic function of isolated Leydig cells was observed, supporting the contention of a CNS-mediated rather than a direct hormone effect. Since increased testicular cyclic adenosine monophosphate (cAMP) produces IS, and a role for the serine proteases plasminogen activators (PAs) in spermiation has been proposed, we examined in vitro BA effects on both Sertoli cell cAMP accumulation and PA activity, respectively.(ABSTRACT TRUNCATED AT 250 WORDS)

Animals↗

The effects of feed restriction on reproductive function in Swiss CD-1 mice.

Many test compounds used in toxicity studies produce a "systemic" toxicity manifested as reduced body weight gain. While it is known that reduced weight gain during juvenile growth reduces or delays reproductive competence, the effects of adult-onset feed restriction (FR) and inhibited weight gain on the reproductive system of mice are poorly known. To gain some information on the effects of graded body weight reduction, or reduced body weight gain, on commonly used reproductive endpoints, the studies reported below were conducted at two laboratories, using adult mice that were maintained at 90, 80, and 70% of concurrent control body weight (CBW) for up to 21 weeks. Estrous cyclicity and fertility in the females were significantly affected. While male fertility was variably affected, there was a significant decrease in the number of epididymal sperm and in the number of testicular spermatids in the 70% CBW groups. Testis weight was conserved in both studies; relative testis weight increased in all FR groups. These data can improve the interpretation of future studies by helping to separate chemically induced changes from those produced by reduced body weight gain.

Animals↗

The effects of feed restriction on reproductive function in Sprague-Dawley rats.

Although it is known that severe feed restriction (FR) and weight reduction (to 50-60% of control values) will sharply impair rat reproduction, few data exist on the effects of less severe body weight reduction. In the present studies, adult Sprague-Dawley rats were feed restricted and maintained at 90, 80, and 70% of control body weight (CBW) for up to 17 weeks. In females, this treatment had no effect on fertility or total number of implants per dam, but transiently increased the length of the estrous cycle and decreased by 20% the number of corpora lutea in the 70% CBW females. Ovary weight at necropsy was decreased only in the 70% CBW group. Liver and kidney weights varied with body weight. In males, fertility was not affected when they were mated to nonrestricted females. While prostate and seminal vesicles weight varied with body weight, testis and epididymis weights were unchanged by any degree of FR, as were the number of sperm in the cauda epididymis and the number of homogenization-resistant spermatids in the testis. The percentage motile sperm was slightly decreased at all levels of FR. These data show that the Sprague-Dawley rat is largely resistant to adverse reproductive changes caused by feed restriction to 70% CBW. These data should be of use in interpreting changes seen in toxicity studies that produce weight-reduce Sprague-Dawley rats.

Animals↗

Are mouse strains differentially susceptible to the reproductive toxicity of ethylene glycol monomethyl ether? A study of three strains.

Most rodent reproductive toxicology studies utilize strains of high fecundity. These studies were conducted to examine the possibility that mouse strains of differing fecundity would respond differently to a known reproductive toxicant. Thirty pairs each of Swiss CD-1, C57B1, and C3H mice were cohabited for 14 weeks while consuming 0, 0.03, 0.10, or 0.30% EGME in the drinking water. Litter data were collected during cohabitation. Body and organ weights, and various sperm data, were collected at necropsy, and second-generation fertility was evaluated. The data show that the most fecund strain (Swiss) was affected the least by exposure to EGME, while the least fecund strain (C3H) suffered the greatest declines in fertility. These differences might alter interspecies extrapolation factors, or the permissible exposure levels for humans.

Animals↗

Analyses of cytogenetic damage in rodents following exposure to simulated groundwater contaminated with pesticides and a fertilizer.

Male Fischer 344 rats and female B6C3F1 mice were each exposed through their drinking water to a mixture of pesticides and ammonium nitrate that simulated contaminated groundwater in California (California Chemical Mixture [CCM]). Exposures were for 71 or 91 days, respectively. In addition, B6C3F1 female mice were exposed for 91 days to another pesticide and ammonium nitrate mixture (Iowa Chemical Mixture [ICM]) through their drinking water. The spleens were removed from the animals, and the splenocytes were cultured for analyses of sister-chromatid exchange (SCE), chromosome aberrations (CA), and micronuclei (MN) in cytochalasin B-induced binucleate cells. A concentration-related increase in SCEs was found in the splenocytes of the rat at the 1x, 10x and 100x levels of the CCM and at the 100x concentration of the CCM in the mouse. There were no other consistent cytogenetic effects observed with the CCM, and no statistically significant cytogenetic damage was observed in mice exposed to the ICM. Evidence from the literature is discussed in order to infer which chemical or chemicals in the CCM might be responsible for the observed SCE response.

Animals↗

Toxicokinetics of [14C]-saligenin cyclic-o-tolyl phosphate in anesthetized male F-344 rats.

Saligenin cyclic o-tolyl phosphate (SCOTP) has been proposed as the active metabolite of tri-o-cresyl phosphate (TOCP), a neurotoxic organophosphate. TOCP is also toxic to the testis and SCOTP mimics some of this toxicity. The stability of SCOTP in vivo and its uptake by selected tissues has been measured. Total radioactivity and SCOTP-associated radioactivity were determined in male F-344 rats treated i.v. with 1 mg of [14C]-SCOTP/kg. The half-life of SCOTP in blood was 8.0 +/- 1.1 min. Testes, brain, and muscle had lower concentrations of [14C]-SCOTP-derived radioactivity than blood. Liver and kidney had higher concentrations of radioactivity than blood. HPLC analysis of liver, kidney, testes, and blood extracts showed that 2.8, 48, 11, and 18%, respectively, of the radioactivity present at 5 min was SCOTP. The amount of SCOTP declined rapidly, and at 30 min SCOTP could be detected only in kidney. It appears that SCOTP, although reactive, has sufficient stability to be transported from organ to organ. There is no evidence, however, of active uptake of SCOTP from blood by the testes. Evidence was obtained that SCOTP may act as an alkylating agent.

Acetylcysteine↗

Testicular and germ cell toxicity: in vitro approaches.

Research on testicular toxicology has been advanced significantly by the introduction of in vitro testing systems. In vivo systems, however, are still essential parts of the risk assessment process, and they are unlikely to be eliminated by in vitro model systems. While in vivo systems are needed to study the integrated male reproductive system, in vitro systems are uniquely suited to investigate specific mechanisms of action in the testis. In vitro systems substantially improve the interpretation and use of in vivo systems. In vitro models can be used alone or in combination with each other to test hypotheses about testicular toxicity. Numerous systems are described in the literature, including Sertoli-germ cell cocultures, Sertoli cell-enriched cultures, germ cell-enriched cultures, Leydig cell cultures, and Leydig-Sertoli cell cocultures. These systems have been used to test relative toxicologic activity of selected chemicals in a class, to investigate the cellular response to certain toxicants, to study the metabolic capability of cells, and to describe the interaction of adjacent cell types.

Drug Evaluation, Preclinical↗

Assessment of a short-term reproductive and developmental toxicity screen.

Short-term tests for reproductive and developmental toxicity are needed to provide preliminary data on the toxicity of chemicals about which little or no data exist. An ideal design would test all aspects of reproduction and identify the target process in a short time period. One potential design has been evaluated using four chemicals of varying reproductive/developmental toxicity. Swiss mice were mated for 3 days prior to chemical exposure to produce time-mated females for gestational exposure and to ascertain fertility of the untreated males. The group of time-mated females was treated during Gestation Days 8-14 and allowed to litter for observations through Postnatal Day (PND) 4. Endpoints observed included pup number and body weights on PND 0, 1, and 4 and number of uterine implantation sites on PND 4. A second group of females was dosed daily for 19 days. After 7 days, these females (n = 10/group) were cohabited with male mice who had been treated for 5 days prior to this second mating. Daily chemical dosing continued during the 5-day cohabitation. This second group of females was killed after 19 days of treatment and the number of live and dead fetuses and implantation sites was recorded. After 17 days of dosing, male mice were killed and the reproductive system evaluated by organ weights, total epididymal sperm counts and motility, and testicular histology. All four chemicals tested, boric acid, ethylene glycol, ethylene glycol monomethyl ether, and theophylline, were found to be toxic to development or reproduction when tested previously by conventional developmental toxicity or continuous breeding protocols. This short-term (21 day) design correctly identified three of these four chemicals as reproductive and developmental toxicants and distinguished the potent toxicants from the less effective compounds. This design can be used to prioritize chemicals for further study, or to delineate the relative toxicities of structurally related chemicals, and to identify the proper dose range for subsequent toxicity studies.

Animals↗

Subchronic (13-week) toxicity studies of oral phenolphthalein in Fischer 344 rats and B6C3F1 mice.

Phenolphthalein is a cathartic agent that is widely used in over-the-counter laxatives. Thirteen-week toxicity studies of phenolphthalein were performed using F344/N rats and B6C3F1 mice. Rats and mice were fed ad libitum with a NIH 07 diet containing 0; 3000; 6000; 12,000; 25,000; or 50,000 ppm phenolphthalein. On a milligram per kilogram body weight basis, rats and mice fed 50,000 ppm phenolphthalein ingested more drug than would be expected during human laxative abuse. Phenolphthalein produced little evidence of toxicity in rats. There was slightly lower weight gain among the 25,000 and 50,000 ppm groups. Treated rats showed elevated relative kidney weights (males only) and elevated absolute and relative liver weights at 12,000-50,000 ppm phenolphthalein. Rat serum bile acids were depressed early (Days 5 and 6) by phenolphthalein treatment. Several treatment-related toxic effects, however, were identified in mice who received more phenolphthalein per unit body weight than rats. Although there were no effects on body weight gain, elevated liver weights were noted in female mice receiving 6000-50,000 ppm phenolphthalein. The primary treatment-related findings that occurred during the mouse studies involved the reproductive and hematopoietic systems. Reproductive changes including depressed testis and right epididymal weights and sperm density, an elevated production of abnormal sperm, and morphologic alterations in seminiferous tubules occurred at all levels of exposure (3000-50,000 ppm). Hematopoietic changes included bone marrow hypoplasia (12,000-50,000 ppm), increased splenic hematopoiesis (males only; 25,000 and 50,000 ppm), and an elevated incidence of micronucleated erythrocytes (6000-50,000 ppm).

Animals↗

Methods for assessing rat sperm motility.

Computer-assisted sperm analysis (CASA) systems are becoming more widely used. With this spread of technology come more data from toxicology studies, designed to determine if treatment with putative toxicants affects sperm motion parameters. While these CASA methods provide us with more ways to evaluate toxicity and thus perhaps increase our chances of successfully protecting human health, there is also a greater likelihood that different laboratories will use different methods of collecting data on sperm motility. Different systems used with different methods in different laboratories will inevitably generate data that are difficult to compare. In a prospective attempt to address this issue of comparability and limit the problems, a group of individuals using CASA systems to analyze rat sperm motility convened to discuss methodologic issues, share data, and try to reach a consensus about methods for performing these studies. This article shares those meetings and data in the hope that common methods will enhance interlaboratory comparisons.

Animals↗

Laboratory methods for assessing human semen in epidemiologic studies: a consensus report.

It is clear that additional methodologic work needs to be performed. Some data gaps described above are being actively investigated. Other standards were not addressed at this meeting; statistical handling of the data, differences among CASA machines, and factors to consider as potential confounders in analysis are just a few. These may be the subject of future workshops, which will also review progress made in the existing knowledge base. For now, this effort represents a first attempt to share information and to use it to encourage investigators in different laboratories to employ similar methods. In this way more direct comparisons among studies can be made, and our collective data base can be strengthened.

Computers↗

The effects of tri-o-cresyl phosphate and metabolites on rat Sertoli cell function in primary culture.

A neurotoxic organophosphate, tri-o-cresyl phosphate (TOCP) is also a testicular toxicant. Histopathologic damage in the testis is first seen in Sertoli cells. TOCP and its activated metabolite saligenin cyclic-o-tolyl phosphate (SCOTP) were evaluated for effects on rat Sertoli cells in primary culture. SCOTP, but not TOCP, caused minor morphologic effects on the cells and increased levels of lactate in the spent medium with no change in pyruvate levels, synthesis of cellular or secreted proteins, or the cyclic AMP response to FSH stimulation. SCOTP was the metabolite of TOCP that produced the largest decrease in nonspecific esterase activity in Sertoli cells (up to 80%), when tested in the concentration range found in vivo. This decrease is consistent with previous in vivo evidence. These in vitro experiments replicate previously observed in vivo biochemical effects and suggest that SCOTP is the metabolite responsible for at least some of the biochemical effects seen in the testis after TOCP exposure.

Adenosine Triphosphate↗

Tissue disposition of boron in male Fischer rats.

Boric acid (H3BO3), an inorganic acid with widespread commercial use and consumer exposure, impairs fertility in male rodents at dose levels lower than those required to cause other adverse effects. Previous studies found a testicular lesion in adult Fischer rats fed 9000 ppm boric acid (1575 ppm boron) and slightly reduced basal serum testosterone levels. A CNS-mediated hormonal component to this lesion was suggested. Detailed data on the tissue disposition of boron in the rat, including accessory sex organs and the brain, are lacking. This study examined the tissue disposition of boron in reproductive, accessory sex organs, and other selected tissues in adult male Fischer rats fed 9000 ppm boric acid to determine if selective accumulation of boron in reproductive tissues, accessory sex organs, and/or the brain might correlate with and explain the apparent selective testicular toxicity. Adult male Fischer rats were fed 9000 ppm boric acid for up to 7 days. Animals were killed at 1, 2, 3, 4, and 7 days after the start of exposure. Plasma and excised tissues were heat-digested in acid and analyzed for boron by inductively coupled argon plasma emission spectrometry (ICAP). With the exception of adrenal glands, control boron levels in all tissues examined were below 4 micrograms/g. There was a rapid increase in plasma and tissue boron 1 day after the start of exposure (range 2- to 20-fold), with the exception of adipose tissue. With the exception of bone and adipose tissue, all soft tissues examined, including the testis, epididymis, accessory sex organs, hypothalamus, and rest of brain, appeared to reach steady-state boron levels (range 12-30 micrograms/g) by 3-4 days. Bone boron levels continued to increase up to the termination at 7 days (40-50 micrograms/g by Day 7). Bone attained the greatest concentration of boron (2- to 3-fold over plasma levels) while levels in adipose tissue were 20% of plasma levels during the 7-day exposure period. All other tissues appeared to show no appreciable accumulation of boron over plasma levels. The data suggest that neither the apparent selective testicular toxicity nor the slight CNS hormonal effect associated with boric acid exposure can be explained on the basis of selective accumulation of boron in the testis or brain/hypothalamus, respectively. Thus, the testicular toxicity is likely the result of certain biological processes that are unique to the testis and which are targets of boron exposure.

Animals↗

Development of testicular lesions in F344 rats after treatment with boric acid.

Boric acid is an inorganic acid that impairs fertility in male rodents. A reproductive assessment by continuous breeding study found that male rats treated with boric acid had decreased fertility and sperm motility. In order to determine the cell type that is first affected by boric acid, we have examined the development of the boric acid-induced testicular lesion by light and electron microscopy. Adult F344 male rats were fed 9000 ppm boric acid in NIH-07 rat chow for up to 4 weeks. The first testicular lesion noted was an inhibition of spermiation, which appeared by Day 7. Widespread exfoliation of apparently viable germ cells, and pachytene cell death in stages VII and XIV, appeared as exposure continued. After 28 days of dosing, extreme epithelial disorganization and germ cell loss were evident. To determine if there was a hormonal component to the boric acid-induced testicular lesion, serum levels of basal, hCG-, and LHRH-stimulated testosterone levels were measured. After 4 days of dosing, basal testosterone levels were lower than controls and remained low during dosing. However, serum testosterone levels were similar in both boric acid-treated and control animals after either hCG or LHRH challenge. To determine if boron was preferentially accumulated by the testis, boron levels in testis, epididymis, liver, kidney, and blood were measured. Boron levels had effectively reached steady-state levels by Day 4 and were not differentially concentrated in the tissues examined. Thus, these studies characterize the testicular lesion produced by boric acid exposure and identify a decrease in basal serum testosterone levels in the absence of selective accumulation of boron in the testis.

Androgen-Binding Protein↗

Light and electron microscopic evidence of tri-o-cresyl phosphate (TOCP)-mediated testicular toxicity in Fischer 344 rats.

The onset and development of testicular lesions following tri-o-cresyl phosphate (TOCP) dosing have been documented through light and electron microscopic morphological studies. Male Fischer 344 rats (190-210 g body weight) were administered 150 mg TOCP/kg/day in corn oil for 1, 3, 5, 7, 10, 14, and 21 days. Vehicle-treated rats served as the control group. Sections of formaldehyde- and glutaraldehyde-fixed, methacrylate-embedded testes showed, by Day 5, numerous spermatid heads apparently detached from tails lying at oblique angles near the basement membrane of the seminiferous tubules. Columnar and spherically shaped vacuoles of the epithelium, radiating from the basement membrane to the lumen of the tubules, were also observed. Electron micrographs revealed that these were localized in Sertoli cells. Widespread dilation of Sertoli cell smooth endoplasmic reticulum was also noted. By 7 days of treatment, residual body abnormalities were noted in stage VIII tubules, along with spermatocyte-derived multinucleated giant cells. The lesion progressed with increased vacuolation of the epithelium and numbers of abnormal residual bodies and giant cells, together with spermatid karyorrhexis (Days 10, 14, and 21). There was also an apparent decrease in sperm density/tubule with continued exposure: 90% of the seminiferous tubules were devoid of sperm by Day 14. These morphological results indicate an initial effect of TOCP on Sertoli cells. Spermatogenesis is affected as seen by the decrease in sperm density and increase in necrotic spermatids.

Animals↗

The effects of ethylene dibromide on semen quality and fertility in the rabbit: evaluation of a model for human seminal characteristics.

Mature (12 months old) male New Zealand White rabbits (8-10/group) were dosed subcutaneously with ethylene dibromide (EDB) in corn oil (untreated and vehicle controls, 15, 30, or 45 mg/kg body wt/day for 5 days). Weekly semen samples (for 6 weeks preexposure, during treatment, and 12 weeks postdosing [pd]) were analyzed for sperm concentration, number, morphology, viability, and motion parameters (velocity, linearity, beat cross-frequency, amplitude of lateral head displacement (ALH), and circularity), and semen pH, osmolality, volume, fructose, citric acid, carnitine, protein, and acid phosphatase (AP). Male fertility was assessed preexposure and at 4 and 12 weeks pd by artificial insemination of three females/male/time point with one million motile sperm. The percentage pregnant females, litter size, fetal body weights, and structural development were assessed. In the 45 mg/kg dose group of males there was 30% mortality and liver damage in 43% of the survivors as evidenced by increased levels of serum enzymes. Also in this group, EDB produced significant decreases in sperm velocity, percentage motility, and ALH (up to 25% at various times pd). There were also dose-related decreases in semen pH (up to 2%) and total ejaculate volume (up to 23%, 15 and 30 mg/kg dose groups only). AP activities were significantly elevated (up to 116%) 2 weeks pd in the 45 mg/kg dose group. All other semen parameters evaluated were unaffected. Male fertility and fetal structural development were also unaffected. Of the seven semen parameters perturbed by EDB in humans (Schrader et al., 1988), four were also affected in the rabbit (sperm velocity, percentage motility, pH, and volume), whereas sperm number, viability, and morphology were not. Thus, some of the male reproductive effects of EDB in the human have been modelled in the rabbit, although the rabbit appears not to be as sensitive, since semen parameters were affected only at doses close to the LD50 (55 mg/kg). The present study (together with other published data) suggests that the rabbit appears to be a potential model for male reproductive toxicity in humans, warranting further evaluation.

Acid Phosphatase↗

Reproductive toxicity assessment by continuous breeding in Sprague-Dawley rats: a comparison of two study designs.

The protocol for Reproductive Assessment by Continuous Breeding (RACB) studies was originally designed to use mice as the test species. However, rats are commonly used for reproductive toxicity research and could be used in the basic RACB design. One of the studies reported below evaluated a standard murine RACB design using rats, which rears the fifth litter to test second generation fertility. The second design tested the logistics and feasibility of rearing the second litter for second generation fertility testing. The standard fifth litter design (L5) was modified slightly for rats by increasing the time allowed for gestation and delivery. Compared to rats rearing their second litter (L2), rats in this L5 design had more litters per pair during continuous breeding and maintained this fertility better over time, as evidenced by producing more pups per litter during the crossover mating segment. Both L2 and L5 rats gave sufficient pups to conduct the second generation fertility evaluation. In addition, the L5 design was easier to conduct and produced pups from gametes exposed to chemical throughout spermatogenesis, making it the preferred design for using rats in Continuous Breeding studies.

Animals↗

Toxicity studies of acetone administered in the drinking water of rodents.

Two- and thirteen-week toxicity studies were conducted using male and female F344/N rats and B6C3F1 mice. Animals were exposed to the following concentrations of acetone in their drinking water: two-week studies 0; 5000; 10,000; 20,000; 50,000; or 100,000 ppm acetone. Thirteen-week rat and female mouse studies 0; 2500; 5000; 10,000; 20,000; or 50,000 ppm acetone. Thirteen week male mice were exposed to 0; 1250; 2500; 5000; 10,000; or 20,000 ppm acetone. Depressed body weight gain was restricted to the 50,000 and 100,000 ppm exposure groups. Male and female mice exposed respectively to 20,000 or 50,000 ppm acetone for 2 weeks developed hepatocellular hypertrophy. This change was not apparent after 13 weeks of exposure although relative and absolute liver weight was increased in high dose female mice. Bone marrow hypoplasia was observed in 5/5 high dose (100,000 ppm) male rats during the 2-week studies. Treatment of male rats for 13 weeks resulted in a variety of mild and subtle hematological changes that often occurred at relatively low levels of exposure (5000 ppm) and resembled those seen during the clinical condition of megaloblastic anemia. Changes characteristic of hypogonadism (depressed sperm motility and cauda epididymal and epididymal weight and elevated incidence of abnormal sperm) were observed in male rats receiving 50,000 ppm acetone for 13 weeks. The incidence and severity of a kidney lesion that is morphologically similar to the spontaneously occurring nephropathy among aging F-344 rats were increased at 20,000 and 50,000 ppm acetone, respectively, in 13-week male rats. In summary, the effects of acetone were either subtle in nature or occurred during very high levels of exposure confirming acetone's low level of toxicity. The daily levels of acetone exposure were often several-fold greater than possibly encountered by humans during the accidental consumption of contaminated groundwater (250 ppm; 5 mg/day) and frequently exceeded maximum levels reported following acute toxic exposures (2,500 mg/kg).

Acetone↗