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Biomedical subjects

R E Chapin

Publications and source records attributed to R E Chapin.

At least 19 recordsLinked to original sources

The effects of dietary boron on bone strength in rats.

Previous studies from our laboratory found that when boric acid (BA) was administered in the diet to rats, boron levels in bone were approximately fourfold greater than serum levels. The current studies were undertaken to determine if these elevations produced adverse effects on several bone-related measures, including serum electrolyte levels, bone structure, and bone strength. Data from two studies are presented: in the first study, young adult male rats consumed a powdered diet containing 0, 3000, 4500, 6000, or 9000 ppm BA for 9 weeks. Endpoints were serum calcium, phosphorous, potassium, and chloride, as well as blood and bone boron concentrations ([B]) measured weekly during the 9-week exposure period, and at 8, 16, 24, and 32 weeks after the end of exposure. In the second study, the male and female young adult rats diet contained 0, 200, 1000, 3000, or 9000 ppm BA for 12 weeks; endpoints measured weekly were serum levels of calcium, phosphorous, and magnesium, bone [B], and bone structure (humerus) and strength (tibia, femur, and lumbar vertebrae). In treated rats, calcium was reduced in the first study but not the second. Serum phosphorous was reduced in both studies; potassium was unchanged, chloride was increased by 1%, and magnesium was reduced in all BA-exposed groups in the second study, to a maximal 19% reduction. Bone [B] was consistently increased in all treated groups, to concentrations approximately fourfold those of serum. After cessation of exposure, serum and urinary boron concentrations dropped to within control values within a week. However, even 32 weeks after the end of exposure, bone [B] remained threefold greater than controls. Male tibia and femur resistance to bending was unchanged. However, vertebral strength in compression was significantly increased by 5-10% in all dose groups (200 to 9000 ppm). The pattern was substantially similar in females. Only the humerus was examined by light microscopy and was found to be unchanged at any level of BA consumption. These data show that, despite a reduction in some serum electrolyte levels, BA consumption increased vertebral resistance to crush force, without detectably altering the microscopic structure of the humerus or the resistance of femur and tibia to a bending load. This increase in compression resistance occurred at exposure levels substantially below those that were previously reported to be reproductively toxic.

Animals

Protection against methoxyacetic-acid-induced spermatocyte apoptosis with calcium channel blockers in cultured rat seminiferous tubules: possible mechanisms.

A calcium-mediated mechanism underlying spermatocyte apoptosis induced by 2-methoxyethanol (2-ME) has been previously proposed. This hypothesis was tested in vitro in the present study using cultured juvenile (25 days old) and adult rat seminiferous tubules (JRST and ARST, respectively) with methoxyacetic acid (MAA, the active metabolite of 2-ME). In JRST, spermatocyte degeneration was morphologically obvious 19 hr after a 5-hr exposure to 5 mM MAA. The lesion was unaffected by the presence or absence of extratubular Ca2+. However, MAA-induced cell death was significantly prevented by cotreatment with the dihydropyridines (DHP) nifedipine (50 microM) and nicardipine (20 microM), as well as verapamil (50 microM) and TMB-8 (50 microM), all of which are able to inhibit calcium movement through plasma membranes. However, neither ryanodine, dantrolene, nor cyclosporin A and ruthenium red, which inhibit Ca2+ mobilization from intracellular stores (endoplasmic reticulum and mitochondria), affected the MAA-induced cell death. Inhibition of calcium mobilization through IP3-sensitive pathways by blocking the product of IP3 with manoalide, neomycin, and U73122 did not block the MAA-induced lesion. The protective effects of 50 microM nifedipine and 50 microM TMB-8 were also observed in ARSTs treated with 10 mM MAA for 5 hr. However, when rat testicular sections were immunohistochemically stained with monoclonal antibodies specific for the alpha 1 (the DHP receptor) or the alpha 2 subunits of DHP-sensitive calcium channels, no positive staining was found. Finally, in an attempt to see whether the intracellular free calcium concentrations ([Ca2+]i) in germ cells were increased after the MAA treatment, intact seminiferous tubules were loaded with indo-1 and were measured using laser-scanning confocal microscopy. No detectable increase in the signal in MA A-sensitive spermatocytes was observed, while a 34-54% increase in the signal could be detected in the same cell types when tubules were exposed to 10 microM of the calcium ionophore 4-bromo-A23187 for 5 min. Collectively, these data suggest that the protective effect of calcium channel blockers against the MAA-induced spermatocyte apoptosis is probably not through their blocking effect on DHP-sensitive calcium channels. We postulate alternate mechanisms based on stabilization of cells membranes, or interactions with calmodulin or protein kinase C.

4-Aminopyridine

Cyclophilin A is present in rat germ cells and is associated with spermatocyte apoptosis. Reproductive Toxicology Group.

Recent investigations in our laboratory revealed divalent cation-dependent endonuclease activity in testes from 2-methoxyethanol-treated rats, which was able to cleave substrate DNA into a pattern of DNA fragmentation consisting of approximately 180-200 base pairs. Further studies were undertaken to characterize the active nuclease. F344 rats were treated with 2-methoxyethanol, a glycol ether that causes the death of pachytene spermatocytes in juvenile and adult rats. The active nuclease was found in nuclear extract from treated animals, but not controls. A radioactive gel nuclease assay, which detects degradation and loss of 32P-labeled DNA from a DNA-containing polyacrylamide gel, localized the nuclease activity to a band of approximately 18 kDa. This activity was dependent on calcium and was inhibited by both zinc and aurintricarboxylic acid. Amino acid sequence data showed that this protein was identical to cyclophilin A. Immunohistochemistry using antibodies against cyclophilin A found specific staining in pachytene spermatocytes, spermatids, interstitial cells, and Sertoli cell nuclei. Cyclophilin A staining was present in both control and 2-methoxyethanol-treated rat testes in a stage-dependent manner, with pachytene spermatocytes in stage-VIII-XIV seminiferous tubules most heavily stained. These data demonstrate that rat testis germ cells contain relatively high levels of cyclophilin A whose nuclease activity is associated with spermatocyte apoptosis induced by 2-methoxyethanol.

Amino Acid Isomerases

Reproductive toxicity of di-n-butylphthalate in a continuous breeding protocol in Sprague-Dawley rats.

The phthalate ester di-n-butylphthalate (DBP) is used extensively in the manufacture of plastics; its reproductive toxicity was tested in rats by the National Toxicology Program's Reproductive Assessment by Continuous Breeding protocol. Levels of 0.1, 0.5, and 1.0% DBP in the diet were selected, and this dosing design yielded average daily DBP intakes of 52, 256, and 509 mg/kg for males and 80, 385, and 794 mg/kg for females, respectively. DBP consumption by F0 rats reduced the total number of live pups per litter in all treated groups by 8-17% and live pup weights in the 0.5% and 1.0% dose groups by < 13%. In tests to determine the affected sex, the number of offspring was unchanged, but the weights of pups from treated females were significantly decreased and offspring from treated males were unchanged. At necropsy, high-dose F0 females had a 14% reduction in body weight, and both sexes had approximately 10-15% increased kidney and liver to body weight ratios compared to controls. Sperm parameters and estrous cyclicity were not affected. In the F1 mating trial, indices of mating, pregnancy, and fertility in the 1.0% dose group were all sharply decreased (one live litter was delivered out of 20 cohabited pairs), concomitant with a 13% decrease in dam body weight. Live F2 pup weights were 6-8% lower in all dose groups. F1 necropsy results revealed that epididymal sperm counts and testicular spermatid head counts were significantly decreased in the 1.0% dose group. Histopathologic investigation showed that 8 of 10 F1 males consuming 1.0% DBP had degenerated seminiferous tubules and 5 of 10 had underdeveloped or otherwise defective epididymides. No ovarian or uterine lesions were observed. In conclusion, this study showed that DBP is a reproductive/developmental toxicant in Sprague-Dawley rats exposed both as adults and during development; it also indicates that the adverse reproductive/developmental effects of DBP on the second generation were greater than on the first generation.

Abnormalities, Drug-Induced

Reproductive assessment by continuous breeding: evolving study design and summaries of ninety studies.

The Reproductive Assessment by Continuous Breeding (RACB) design has been used by the National Toxicology Program for approximately 15 years. This article details the evolutions in the thinking behind the design and the end points used in the identification of hazards to reproduction. Means of nominating chemicals are provided, and both early and current designs are described as well as some proposed changes for the future. This introduction is followed by a text and tabular summary of each study performed to date. We hope that this will not only be an explicit presentation of the findings of this testing program to date, but will help stimulate thinking about new ways to detect and measure reproductive toxicity in rodents, and help identify new relationships among the end points that are measured in such studies.

Acrylamides

Studies on the reproductive effects of Fusarium moniliforme culture material in rats and the biodistribution of [14C] fumonisin B1 in pregnant rats.

Fumonisins are mycotoxins produced by Fusarium moniliforme and other Fusarium species. They are commonly found in corn and corn-based foodstuffs. Fumonisins inhibit sphingolipid (SL) biosynthesis, alter cellular SL profiles, and thus may affect cell proliferation and differentiation, both of which are important processes for reproduction. However, there are few reports of the effects of F. moniliforme or fumonisins on mammalian reproduction or development. To study the reproductive effects of this fungus, diets formulated with culture material of toxic F. moniliforme strain MRC 826 (CM) to provide 0, 1, 10, or 55 ppm fumonisin B1 (FB1) were fed to male and female rats beginning 9 and 2 weeks before mating, respectively, and continuing throughout mating, gestational, and lactational phases of the study. CM caused nephropathy, typical of FB1, in males fed > or = 10 ppm and females fed 55 ppm FB1. No significant reproductive effects were found in males (n = 12/group), dams, and fetuses examined on gestation day 15 (G15) (n > or = 8/group), or dams and litters through day 21 postpartum (n > or = 9/group). Litter weight gain in the 10 or 55 ppm FB1 groups was slightly decreased; however, gross litter weight and physical development of offspring were not affected. Altered SL ratios indicative of fumonisin exposure, specifically increased sphinganine to sphingosine ratios, were found in the livers of dams from the 55-ppm FB1 group on G15. However, SL ratios of abdominal slices, containing liver and kidney, of fetuses from control and high-dose litters did not differ. In a second experiment, two dams were injected intravenously on G15 with 101 micrograms [14C]FB1 (3.179 x 10(5) dpm). After 1 hr, which allowed for ca. 98% of the dose to be cleared from the maternal blood, negligible amounts of radioactivity were found in the fetuses. Together, these results indicate that the CM, and by inference FB1, did not have significant reproductive effects at doses which are minimally toxic, and further suggest that little in utero FB1 exposure occurred through G15.

Animals

Endocrine modulation of reproduction.

The ability of foreign compounds to affect the functioning of various endocrine systems is currently thought responsible for a wide variety of effects. The presentations in this Symposium reviewed the evidence for and against the involvement of endocrine systems in several different aspects of reproduction. The mechanism behind the ability of a triazine herbicide to cause enhanced appearance of mammary tumors in one strain of female rats is reviewed by Stevens. The data suggest that enhanced aging, not direct mammary modulation, is responsible. Dietary phytoestrogens, the mediators of their actions, their effects in various biological systems, and the relationships between phytoestrogen producers and consumers are all provocatively and succinctly reviewed by Hughes. Kelce presents the strategy used to dissect the mode and mechanisms of action of a fungicide that opened a new awareness in reproductive toxicology: the possibility of xenobiotics being antiandrogens. Finally, to heighten our understanding of the interplay among hormonal systems in vivo, Hess reviews the data that show that androgens are not the only hormones important in the development of the male reproductive system: the pituitary is shown to play a critical role at specific stages of development. The breadth of these presentations, and the implications of their findings, should make us pause and realize how much there is still to discover about the interaction between the reproductive system and anthropogenic compounds.

Aging

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

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

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

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

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

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

Assessment of the reproductive and developmental toxicity of pesticide/fertilizer mixtures based on confirmed pesticide contamination in California and Iowa groundwater.

Pesticides and fertilizers, as used in modern agriculture, contribute to the overall low-level contamination of groundwater sources. In order to determine the potential of pesticide and fertilizer mixtures to produce reproductive or developmental toxicity at concentrations up to 100 x the median level found in groundwater, we prepared and studied two mixtures of pesticides and a fertilizer (ammonium nitrate). One mixture containing aldicarb, atrazine, dibromochloropropane, 1,2-dichloropropane, ethylene dibromide, and simazine plus ammonium nitrate was considered to be a representative of groundwater contamination in California (CAL). The other, containing alachlor, atrazine, cyanazine, metolachlor, metribuzin, and ammonium nitrate, simulated groundwater contamination in Iowa (IOWA). Each mixture was administered in the drinking water of either Swiss CD-1 mice during a Reproductive Assessment by Continuous Breeding study or pregnant Sprague-Dawley rats (gd 6-20) at three dose levels (1x, 10x, and 100x) where 1x was the median concentration of each pesticide component as determined in the groundwater surveys in California or Iowa. Unlike conventional toxicology studies, the purpose of this study was to evaluate the health effects of realistic human concentrations. Thus, the testing concentrations are probably well below the maximally tolerated dose. Propylene glycol was used as the solubilizer for the pesticides in drinking water formulations in both studies. In the reproductive study, neither mixture caused any clinical signs of toxicity, changes in food or water consumption, or body weight in either F0 or F1 mice at doses up to 100x the median groundwater concentrations. There were no treatment-related effects on fertility or any measures of reproductive performance of either the F0 or the F1 generation mice exposed to either CAL or IOWA at up to 100x. Similarly, measures of spermatogenesis, epididymal sperm concentration, percentage motile sperm, percentage abnormal sperm, and testicular and epididymal histology were normal. In the developmental study, CAL- or IOWA-exposed females did not exhibit any significant treatment-related clinical signs of toxicity. No adverse effects of CAL or IOWA were observed for measures of embryo/fetal toxicity, including resorptions per litter, live litter size, or fetal body weight. CAL or IOWA did not cause an increased incidence of fetal malformations or variations. In summary, administration of these pesticide/fertilizer mixtures at levels up to 100-fold greater than the median concentrations in groundwater supplies in California or Iowa did not cause any detectable reproductive (mice), general, or developmental toxicity (rats).

Animals

The reproductive toxicity of boric acid.

Previous studies on the reproductive toxicity of boric acid have indicated that male rodents suffer testicular atrophy after treatment. There were, however, no studies of the potential effects on female fertility or on the neonate. In addition, no study described the development of the testicular lesion, thought to be related to the mechanism of toxicity. A Reproductive Assessment by Continuous Breeding (RACB) study using mice exposed to boric acid at 1000, 4500, and 9000 ppm in the diet indicated that there are probably multiple sites of action, although male fertility appears very sensitive. Possible effects on female fertility cannot be separated from potential developmental toxicity and need additional investigation. Decrements in sperm motility were observed at all exposure levels, and testicular atrophy was confirmed in high- and middle-dose-group males. This was investigated further by timed serial-sacrifice studies using 9000 ppm in the diet of rats, which found that the first lesion seen in the testis was an inhibition of spermiation (release of mature spermatids). With continued dosing, this was followed by a disorganization of the normal ordered layering of the seminiferous epithelium, germ cell sloughing and death, and finally, atrophy. Subsequent studies using additional doses (2000, 3000, 4500, 6000, and 9000 ppm) found that it was possible to observe inhibited spermiation that did not progress to atrophy (4500 ppm and below) within the 9-week exposure period.(ABSTRACT TRUNCATED AT 250 WORDS)

Animals

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