Biomedical subjects

R E Chapin

Publications and source records attributed to R E Chapin.

At least 19 recordsLinked to original sources

PubMed1995

Assessment of the reproductive toxicity of a complex mixture of 25 groundwater contaminants in mice and rats.

The potential reproductive toxicity of a mixture of 25 chemicals (MIX) formulated to simulate contaminated groundwater supplies near hazardous waste dumps was evaluated in CD-1 Swiss mice and Sprague-Dawley rats using the reproductive assessment by continuous breeding protocol. Male and female mice and rats were exposed to MIX in the drinking water at concentrations of 1, 5, and 10% of a technically achievable stock solution. For mice, body weight and feed consumption were not affected by MIX but water consumption was decreased for both the 5 and 10% MIX groups in both F0 and F1 animals. For F0 mice, the number of live pups/litter was decreased at 10% MIX and the number of females/litter was decreased 10 and 17% at the mid and high MIX dose, respectively. Vaginal cytology was normal, as were testis weight and testicular spermatid head count. For F1 mice, fertility was unaffected, but there was a decreased number of female pups/litter (19%) and a decreased adjusted live pup weight at 10% MIX. At necropsy, cauda epididymal sperm concentration and spermatid head count were reduced (20%) in the presence of normal testis, epididymis, prostate, seminal vesicle, liver, and kidney/adrenal weight. Female estrous cyclicity was altered at 5 and 10% MIX with normal kidney/adrenal, uterus, and ovary/oviduct weight. For rats, F0 body weight and feed consumption were not affected by MIX but water consumption was decreased 10, 30, and 40% in the low-, medium-, and high-dose MIX groups, respectively, and 39% in the high-dose MIX F1 animals. Rat fertility was normal but there was a decreased number of male pups/litter (11%) and a decreased live pup weight (6%) at 10% MIX. Male and female (F1) pup weights were decreased on Postnatal Days 0, 4, 7, 14, and 21 (10% MIX) and remained lower through necropsy on Day 120 +/- 10. F1 fertility was normal but F2 pup weights were decreased (10% MIX). At necropsy, F1 (10% MIX) male body weight was decreased 16% and relative kidney, testis, epididymis, and prostate weights were increased in the presence of normal sperm concentration percentage motile sperm and percentage abnormal sperm. Estrous cyclicity was normal as were kidney/adrenal and ovary weight while female liver weight was reduced 14%. In summary, a "cocktail" of 25 chemicals commonly found in contaminated groundwater at or near hazardous waste sites was administered in drinking water at doses which resulted in severely decreased water consumption in both mice and rats.(ABSTRACT TRUNCATED AT 400 WORDS)

Animals↗

PubMed1995

The reproductive and neural toxicities of acrylamide and three analogues in Swiss mice, evaluated using the continuous breeding protocol.

Acrylamide is a known genetic, reproductive, and neural toxicant, although it is not known if one effect is predominant. The toxicities of several structural analogues of acrylamide have been incompletely characterized, and the relative sensitivity of the second generation is not known. The present studies were designed to explore the relationship between neurotoxicity and reproductive toxicity, to further characterize the toxicities of three acrylamide analogues, and to evaluate the relative sensitivity of a second generation to these compounds. For the F0 generation, male and female Swiss CD-1 mice were provided drinking water containing acrylamide (ACR; 3, 10, 30 ppm), N,N'-methylenebisacrylamide (MBA; 10, 30, 60 ppm), N-(hydroxymethyl)acrylamide (HMA; 60, 180, 360 ppm), or methacrylamide (MACR; 24, 80, 240 ppm) during and after a 14-week cohabitation. The last litter was reared and dosed after weaning until mating at 74 +/- 10 days of age with the same level of compound given to the parents Neurotoxicity was assessed at several times in both generations by measuring forelimb and hindlimb grip strength. In the F0 generation, ACR caused an 11% decrease in pup number without measurable neurotoxicity; female fertility was not affected. Although both generations consumed the same amount of ACR, there were larger changes in the fertility-related endpoints in the F1 mice than in the F0's, with no concomitant change in organ weights or sperm parameters. In F0 mice, MBA reduced the number of live pups and their adjusted weight, with no neurotoxicity and no change in F0 female reproduction. MBA caused greater adverse effects in the second generation, concomitant with increased consumption. In the F0 generation, HMA caused the largest decrease in pup number during cohabitation (26%) together with a small effect on grip strength. Female reproduction was not affected. The second generation consumed more HMA and showed slightly greater toxic effects. In both generations, MACR was negative for both neurotoxicity and reproductive toxicity. Dominant-lethal studies showed that the fertility effects for ACR, MBA, and HMA could be explained by a male-mediated increase in postimplantation loss. These studies found that dominant lethality occurred without structural effects on the reproductive system in the presence of only minor effects on grip strength and without detectable neural histopathology. Female reproduction was not significantly affected by these compounds at the doses used. Thus, these data confirm the male as the affected gender and that the reproductive toxicity was greater than motoneuron toxicity when measured as grip strength.

Acrylamide↗

PubMed1995

The reproductive and developmental toxicity of indium in the Swiss mouse.

Indium is increasingly used in a variety of industries, and while there are few studies of its developmental toxicity, ther are no reports of its potential reproductive toxicity. These studies were undertaken to investigate the possible reproductive toxicity of indium and to determine the relative vulnerability of males and females. We used, initially, a 21-day combined developmental/reproductive toxicity protocol. Oral exposures to InCl3 ( < or = 250 mg/kg) were without effect on the male reproductive system or liver. A kidney effect was demonstrated in males by a decrease in urinary N-acetyl glucosaminidase. The ability of females to become pregnant was unaffected. However, fetal development was adversely affected, manifested as increased intrauterine deaths in the presence of reduced maternal weight gain. A developmental toxicity study identified no increase in fetal malformations, but verified the increased fetal deaths, in the absence of effects on adjusted maternal body weight. In vitro toxicity studies showed that the embryolethality was at least in part a result of direct toxicity to the conceptus, with effective doses in the low micromolar range. A limited disposition study showed that fetuses contained low micromolar concentrations of indium, more indium than maternal liver, and comparable to levels that were toxic in vitro. Although studies of greater exposure duration are required for risk assessment, these data indicate that fetal development is likely to be more affected by indium than female or male reproduction, with adverse effects occurring at low micromolar levels in vivo and at exposures that may or may not affect body weight.

Abnormalities, Drug-Induced↗

PubMed1995

Spermatocyte toxicity of 2-methoxyethanol (ME) in rats and guinea pigs: evidence for the induction of apoptosis.

2-Methoxyethanol (ME) produces testicular lesions characterized by pachytene spermatocyte degeneration in rats and guinea pigs which differ in onset, severity, and morphological characteristics. In the rat, degenerating spermatocytes appear necrotic at 24 hr, while in the guinea pig they appear apoptotic 96 hr after the start of three daily doses. To further examine if the spermatocyte degeneration in both species represented necrosis or apoptosis, the extent and nature of nuclear DNA fragmentation after ME exposure were assessed both visually using an in situ nucleotide 3' end-labeling (ISEL) procedure and by DNA gel electrophoresis. Testes from rats given a single oral dose of ME (200 mg/kg) showed the expected pachytene spermatocyte degeneration 24 hr after dosing, with the nuclear chromatin degradation typical of necrosis. In contrast, testes from guinea pigs given daily oral doses of ME (200 mg/kg) showed spermatocyte degeneration at only 96 hr after the start of dosing, with marked peripheral nuclear chromatin condensation characteristic of apoptosis. Coincident with the appearance of morphologic changes, degenerating spermatocytes in both species contained fragmented DNA as revealed by the ISEL procedure. The pattern of DNA fragmentation on agarose gels in both species consisted of ordered multiples or "ladders" of approximately 200 base pairs, a hallmark of apoptosis, with their appearance coincident with the time course of morphologic spermatocyte degeneration and ISEL staining. Preliminary data reveal the appearance of divalent metal cation-dependent endonuclease activity at pH 7.0 in ME-treated immature (24-day-old) rat testis that produces a similar pattern of DNA fragmentation and which appears to be distinct from activity associated with the spontaneous germ cell degeneration observed in testes of this age. In summary, in vivo ME exposure induces spermatocyte apoptosis in both the rat and guinea pig despite differing morphological classifications and time of onset of cell death. Future studies will focus on further characterization of the testicular endonuclease in the rat and the potential role of increased intracellular Ca2+ as a "triggering" stimulus in ME-induced spermatocyte apoptosis.

Animals↗

PubMed1995

Histologic localization of surgically transplanted syngeneic seminiferous tubule segments into testis with Fast Blue as tracer.

Spermatogenesis is a complex differentiative process influenced by the testicular extratubular and intratubular tissue environments. One method of determining the relative importance of intratubular versus extratubular factors in cases of deficient spermatogenesis has been syngeneic seminiferous tubule transplantation. Generally in such a scheme, tubule segments from a testis deficient in spermatogenesis are transplanted into an intact recipient testis, and the progression of spermatogenesis in transplanted tubules is examined histologically. However, this experimental approach has been complicated by the tedious histologic serial sectioning required to locate these transplanted tubules and the need to distinguish them from recipient testis solely by structural differences. A method is described for the surgical transplantation of seminiferous tubule segments into rat testes that uses prelabeling donor tubules in vitro with the fluorescent tracer Fast Blue to facilitate their localization. The technique was evaluated by transplanting cut segments of Fast Blue-labeled seminiferous tubules from 15-day-old rat testis into normal adult rat testis (recipient), then localizing and histologically examining the progression of spermatogenesis in the transplanted tubules for up to 28 days. Transplanted tubules were easily identified in sections of recipient testis by fluorescent microscopy; intense Fast Blue staining with low background was seen up to 28 days after transplantation. Histologically, transplanted tubules had limited germ cell differentiation in recipient testis for the Fischer rat strain. At 10 days after transplantation, tubules had characteristics qualitatively similar to tubules from 25-day-old rat testis, with increased tubular diameter and abundant germ cells at the pachytene spermatocyte stage.(ABSTRACT TRUNCATED AT 250 WORDS)

Amidines↗

PubMed1994

Comparison of the testicular effects of 2-methoxyethanol (ME) in rats and guinea pigs.

Glycol ethers produce both hemato- and testicular toxicity in animals, which is dependent on both the alkyl chain length and animal species used. Ethylene glycol monobutyl ether (2-butoxyethanol, BE) causes hemolytic anemia in rats but not in guinea pigs, and red blood cells from both guinea pigs and humans are minimally affected in vitro by the active metabolite 2-butoxyacetic acid. This demonstrates the importance of animal species selection for assessing human risk to BE exposure. 2-Methoxyethanol (ME) produces testicular lesions in rats characterized primarily by the degeneration of spermatocytes undergoing meiotic division with minimal or no hemolytic changes. Because of the differential hemolytic response to BE between rats and guinea pigs, the present study addressed whether the testicular response to ME was similarly dichotomous. Adult rats or guinea pigs were given a single dose of either 200 or 300 mg ME/kg by gavage, and testicular and hemolytic changes were assessed 24 hr after treatment. Testis histology in rats showed dose-dependent degeneration of dividing spermatocytes in stage XIV tubules as expected, with only minimal hemolytic changes, also as expected. In contrast, no testicular or hemolytic effects were observed in guinea pigs 24 hr after either single ME dose. In a subsequent study, a single dose or multiple (3 daily) doses of 200 mg ME/kg were given, and animals were examined at 4 days after the start of treatment. Testes from rats given both single and multiple ME doses showed, as expected, tubules depleted of spermatocytes and early spermatids. In guinea pigs, spermatocyte degeneration was observed in stage III/IV tubules for both dosing schemes, but was much less severe and widespread and differed from rats in morphological characteristics, specifically in the appearance of nuclear chromatin degeneration. In the rat, degenerating spermatocytes showed uniformly condensed and dispersed chromatin, while in the guinea pig they showed marked chromatin condensation at the nuclear periphery. No hemolytic changes were observed in either species or dosing scheme. In summary, although ME-associated testicular lesions were observed in both species, they differed significantly in onset, characteristics, and severity. Both the nature of the differential testicular response to ME and a comparison to the in vitro human testicular response to the active metabolite 2-methoxyacetic acid are subjects of future study.

Animals↗

PubMed1993

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↗

PubMed1992

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↗

PubMed1992

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↗

PubMed1992

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↗

PubMed1992

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↗

PubMed1991

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↗

PubMed1991

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↗

PubMed1991

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↗

PubMed1991

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↗

PubMed1991

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↗

PubMed1991

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↗

PubMed1991

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↗