Three-generation reproductive toxicity study of dietary bisphenol A in CD Sprague-Dawley rats.

Bisphenol A (BPA) was evaluated at concentrations of 0, 0.015, 0.3, 4.5, 75, 750, and 7500 ppm ( approximately 0.001, 0.02, 0.3, 5, 50, and 500 mg/kg/day of BPA) administered in the diet ad libitum to 30 CD((R)) Sprague-Dawley rats/sex/dose for 3 offspring generations, 1 litter/generation, through F3 adults. Adult systemic toxicity at 750 and 7500 ppm in all generations included: reduced body weights and body weight gains, reduced absolute and increased relative weanling and adult organ weights (liver, kidneys, adrenals, spleen, pituitary, and brain), and female slight/mild renal and hepatic pathology at 7500 ppm. Reproductive organ histopathology and function were unaffected. Ovarian weights as well as total pups and live pups/litter on postnatal day (PND) 0 were decreased at 7500 ppm, which exceeded the adult maximum tolerated dose (MTD). Mating, fertility, gestational indices; ovarian primordial follicle counts; estrous cyclicity; precoital interval; gestational length; offspring sex ratios; postnatal survival; nipple/areolae retention in preweanling males; epididymal sperm number, motility, morphology; daily sperm production (DSP), and efficiency of DSP were all unaffected. At 7500 ppm, vaginal patency (VP) and preputial separation (PPS) were delayed in F1, F2, and F3 offspring, associated with reduced body weights. Anogenital distance (AGD) on PND 0 was unaffected for F2 and F3 males and F3 females (F2 female AGD was increased at some doses, not at 7500 ppm, and was considered not biologically or toxicologically relevant). Adult systemic no observed adverse effect level (NOAEL) = 75 ppm (5 mg/kg/day); reproductive and postnatal NOAELs = 750 ppm (50 mg/kg/day). There were no treatment-related effects in the low-dose region (0.001-5 mg/kg/day) on any parameters and no evidence of nonmonotonic dose-response curves across generations for either sex. BPA should not be considered a selective reproductive toxicant, based on the results of this study.

Comparison of the developmental and reproductive toxicity of diethylstilbestrol administered to rats in utero, lactationally, preweaning, or postweaning.

The objective of the study was to determine which period of exposure produces the most marked effects on the reproductive capacity and sexual development of the rat, with particular emphasis on the relative sensitivity of in utero and postnatal exposures. The endocrine active chemical, diethylstilbestrol (DES) was used as an agent known to affect many of the endpoints examined. Hitherto, such comparisons have been made between studies, rather than within a study. Our data will be helpful in the interpretation of future multigenerational assay data. In preliminary studies, DES was shown to be active in the immature rat uterotrophic assay with a lowest detected dose of 0.05 mg DES/kg body weight by sc injection and 10 mg DES/l (1.6 mg DES/kg body weight) by administration in drinking water. A dose of 60 microg DES/l drinking water ( approximately 6.5mg DES/kg body weight/day) was selected for the main study since this represented the midpoint of the drinking water uterotrophic dose response and produced no overt maternal toxicity. The study used 10 groups of concomitantly pregnant animals, including 2 control groups. The first comparison was between the effects of exposure to DES in utero, and exposure from conception to weaning. Another group of animals was exposed to DES in utero and cross-fostered to untreated pregnant females to prevent lactational transfer of DES to pups. Two groups were exposed to DES neonatally, either from birth to postnatal day (PND) 10 (pups thus having only lactational exposure), or from birth until weaning (PND 21; pups thus having both lactational exposure and self-exposure via drinking water). In addition, a dose response study to DES was conducted on animals exposed from weaning to PND 100, when the first phase of the study was terminated. Pups exposed to DES in utero and pups exposed from weaning to PND 100 were bred to assess fertility of the F1 animals and the sexual development of F2 offspring. This last comparison was to determine the extent to which weanling rats could be used in endocrine toxicity studies to assess their potential to show activity in utero. The most sensitive period of exposure for inducing developmental effects in F1 animals was from weaning onwards. The neonatal to weaning period (PND 1-21) was the next most sensitive. Essentially no effects were induced in F1 animals exposed in utero. No effects of any kind were observed in animals only exposed over the early neonatal period of PND 1-10. The mean day of vaginal opening, testes descent, and prepuce separation was only altered in groups where postnatal exposure to DES continued beyond PND 10, or was started at weaning. No changes were observed in anogenital distance or caudal sperm counts. Some changes in organ weights were observed, but the interpretation of these was often confused by concomitant changes in body weight. In general, histopathological examination of tissues yielded no additional information. In breeding studies with animals exposed to DES in utero, or from weaning, reduced litter sizes and marginal advances in the day of vaginal opening were observed in the offspring, together with changes in organ weights. However, no unique sensitivity was noted for exposure in utero. Evaluation of the several exposure periods and the many markers monitored in this study may have individual strengths in individual cases, but when rigorously compared using the reference estrogen DES, many preconceptions regarding their absolute or relative value were not upheld. Further, each of these markers is subject to natural variability, as demonstrated by comparisons made among the 5 separate control groups available in parts of the present study. This variability increases the chance that small changes observed in endocrine toxicity studies employing small group sizes and a single control group, or no concomitant control group, may be artifactual. The most marked effects observed in this study were on the developmental landmarks in the F1 animals induced by exposures after PND 10. Some effects on developmental landmarks and organ weights were observed in F2 animals following exposure either in utero or postweaning. This study therefore does not establish a unique role for exposures in utero or during the early neonatal period.

Effect of rodent diets on the sexual development of the rat.

Five rodent diets have been evaluated for their possible effect on the sexual development of the rat. Groups of 12 pregnant Alpk rats were fed one of the following combinations of diets during pregnancy and postnatally: RM3/RM1, AIN-76A/AIN-76A, RM3/AIN-76A, Teklad Global 2016 (Global)/Global and Purina 5001/Purina 5001. AIN-76A is phytoestrogen-free while the other diets contained varying amounts of phytoestrogens. The phytoestrogens genistein and daidzein were determined in the diets studied, and the concentrations found agreed with earlier estimates. RM3/RM1 was selected as the control group, as this has been used routinely in this laboratory for the past decade. Determinations were made in offspring of the times of vaginal opening and first estrus among the females, and of prepuce separation and testes descent among the males. At postnatal day (PND) 26 the females from 6 of the 12 litters were terminated and tissue weights measured. Males from 6 of the 12 litters were similarly studied at PND 68. Animals from the remaining litters were transferred to RM1 diet at PND 70. Termination of the study was at PND 128 (males) and PND 140 (females) when body weights and tissue weights were determined. Marked differences in body weight, sexual development, and reproductive tissue weights were observed for rats maintained on AIN-76A or Purina 5001, with only minimal effects among rats maintained on the Global diet. These comparisons were against RM3/RM1 as the reference diet. However, using Purina 5001 as the reference diet reversed the direction of the differences seen when using RM3/RM1 as the reference diet. The differences observed when using RM3/RM1 as reference diet occurred mainly postnatally. In addition, the fact that similar differences were seen for the phytoestrogen-free diet, AIN-76A, and the phytoestrogen-rich diet, Purina 5001, indicate that these effects are more likely to be caused by nutritional differences between the diets that then have centrally mediated effects on rodent sexual development, rather than individual dietary components affecting peripheral estrogen receptors (ER). This proposal is supported by abolition of the uterotrophic activity of AIN-76A and Purina 5001 (relative to RM3/RM1) in the immature rat by coadministration of the gonadotrophin-releasing hormone (GnRH) antagonist ANTARELIX: The present data indicate that choice of diet may influence the timing of sexual development in the rat, and consequently, that when evaluating the potential endocrine toxicity of chemicals, the components of rodent diets used should be known, and as far as is possible, controlled.

Comparative in vitro percutaneous absorption of nonylphenol and nonylphenol ethoxylates (NPE-4 and NPE-9) through human, porcine and rat skin.

The purpose of this study was to assess the percutaneous absorption of nonylphenol (NP) and the nonylphenol ethoxylates, NPE-4 and NPE-9, in human, porcine and rat skin. In vitro studies with the NPEs were conducted for 8 h in flowthrough diffusion cells using topical solutions of 0.1, 1.0 and 10% in PEG-400 or 1% in water (NPE-9 only). NP absorption was assessed as a 1% solution in PEG-400. All compounds were 14C ring-labeled and radioactivity in perfusate was monitored over time. Skin deposition was measured at the termination of the experiment. Absorption into perfusate and total penetration (compound absorbed plus compound sequestered in skin) were calculated. Absorption of NPE-4, NPE-9 and NP was similar across all species at less than 1% of the applied dose over 8 h. Penetration was generally below 5% of applied dose, the majority located in the stratum corneum. In all species and for both NPEs, the fraction of dose absorbed was highest for the lowest applied dose. Absorptions expressed as actual mass absorbed over 8 h were similar (approximately 0.3 microg/cm2) across all concentrations. Penetration, but not absorption, was greater from a water vehicle compared to a PEG-400 vehicle, particularly in rat skin. These studies suggest that NP, NPE-4 and NPE-9 were minimally absorbed across skin from all three species. Fractional absorption was concentration-dependent, making the actual absorbed flux constant across all doses.

Effects of p-nonylphenol (NP) and diethylstilboestrol (DES) on the Alderley Park (Alpk) rat: comparison of mammary gland and uterus sensitivity following oral gavage or implanted mini-pumps.

An earlier report by Colerangle and Roy indicated that administration of p-nonylphenol (NP) to Noble rats, via subcutaneously implanted mini-pumps at estimated doses of 53.2 and 0.073 mg kg(-1) day(-1) for 11 days, led to proliferation of the mammary gland. Those results indicated a ca. 600-fold enhancement in assay sensitivity to NP over that of the standard 3-day rat uterotrophic assay. The potential importance of these observations led us to repeat the experiments in the Noble rat, as described earlier. Although our earlier results confirmed the reported effects of diethylstilboestrol (DES) on the mammary gland of Noble rats, we found no effects with NP. The present report extends our investigations of the effects of NP and DES on the mammary gland and uterus of other rat strains using both oral dosing and exposure via mini-pumps. The 3-day oral uterotrophic assay responses to NP were similar for immature Alderly Park (Alpk; Wistar-derived) and immature Sprague-Dawley rats. Likewise, oral administration of NP to ovariectomized Alpk rats for 11 days gave responses of a similar magnitude to those seen in the 3-day immature assays and in earlier 3-and 11-day oral assays conducted using Noble rats. Administration of NP via mini-pumps to ovariectomized Alpk rats, at the implant doses employed by Colerangle and Roy, gave a negative uterotrophic response. The highest achieved dose levels of NP in the implant experiment (27 mg kg(-1) day(-1)) were lower than in the above assays and the negative response was therefore consistent with the previously defined minimum detection level for NP in the uterotrophic assay of ca. 40 mg kg(-1) day(-1) day(-1). It is concluded that the uterotrophic activity of NP is independent of the strain of rat, the duration of dosing and the route of exposure. Two mammary gland studies were conducted on NP and DES in the Alpk rat. In the first study (a repeat of the techniques used in earlier studies with the Noble rat), NP was administered via mini-pumps (achieved doses of 0.052 and 37.4 mg kg(-1) day(-3) NP) and produced no effect on mammary gland development, whereas DES gave the expected trophic response. In the second mammary gland study, NP was administered orally to Alpk rats at 100 mg kg(-1) day(-1) for 11 days (a dose that produced a positive uterotrophic response in ovariectomized rats). In this experiment, DES, and to a lesser extent NP, increased mammary gland differentiation and cell proliferation. The present studies have demonstrated that the rat mammary gland responds predictably to oestrogenic stimulation but does not show increased sensitivity to oestrogens when compared to the rat uterus. It is also concluded that the minimum detection level for oestrogenic responses of NP in rodents, following oral, dietary and implant routes of exposure, is ca. 40 mg kg(-1) day(-1).

Normal reproductive organ development in Wistar rats exposed to bisphenol A in the drinking water.

Bisphenol A (BPA) is a chemical used primarily as a monomer in the manufacture of numerous chemical products, such as epoxy resins and polycarbonate. The objective of this study was to evaluate potential effects of BPA on sexual development of male rats and was designed to clarify low-dose observations reported as preliminary results by Sharpe et al. (1996). The protocol for the present study followed the same treatment schedule as reported by Sharpe et al. (1995, 1996), but included more treatment groups, a greater number of animals per group, and a more comprehensive number of reproductive endpoints. Groups of 28 female Han-Wistar albino rats were exposed to drinking water that contained 0, 0.01, 0.1, 1.0, or 10 ppm BPA or 0.1 ppm diethylstilbestrol (DES), 7 days per week, for a total of 10 weeks. Treatment of the females began at 10 weeks of age and continued throughout a 2-week premating period, 2 weeks of mating (to untreated males), 21-22 days of gestation, and 22 days of lactation. Offspring weanling males were given untreated drinking water and maintained until 90 days of age when evaluations were made of various reproductive organs. Consistent with Sharpe et al. (1996) the female offspring were not evaluated. No treatment-related effects on growth or reproductive endpoints were observed in adult females exposed to any concentration of BPA. Similarly, no treatment-related effects were observed on the growth, survival, or reproductive parameters (including testes, prostate and preputial gland weights, sperm count, daily sperm production, or testes histopathology) of male offspring from dams exposed to BPA during gestation and lactation. DES administered in the drinking water at 0. 1 ppm resulted in decreased body weight, body weight change, and food consumption in adult females. In addition, an increase in the duration of gestation and a decrease in the number of pups delivered and number of live pups were also observed in animals exposed to DES. In conclusion, these results do not confirm the previous findings of Sharpe et al. (1996) and show that low doses of BPA had no effects on male sexual development in the rat.

Normal reproductive organ development in CF-1 mice following prenatal exposure to bisphenol A.

Bisphenol A (BPA) is a monomer used in the manufacture of a multitude of chemical products, including epoxy resins and polycarbonate. The objective of this study was to evaluate the effects of BPA on male sexual development. This study, performed in CF-1 mice, was limited to the measurement of sex-organ weights, daily sperm production (DSP), epididymal sperm count, and testis histopathology in the offspring of female mice exposed to low doses of BPA (0, 0.2, 2, 20, or 200 microg/kg/day), by deposition in the mouth on gestation days 11-17. Male sexual development determinations were made in offspring at 90 days-of-age. Since this study was conducted to investigate and clarify low-dose effects reported by S. C. Nagel et al., 1997, Environ. Health Perspect. 105, 70-76, and F. S. vom Saal et al., 1998, Toxicol. Indust. Health 14, 239-260, our study protocol purposely duplicated the referenced studies for all factors indicated as critical by those investigators. An additional group was dosed orally with 0.2 microg/kg/day of diethylstilbestrol (DES), which was selected based on the maternal dose reported to have maximum effect on the prostate of developing offspring, by F. S. vom Saal (1996, personal communication), vom Saal et al. (1997, Proc. Natl. Acad. Sci. U S A 94, 2056-2061). Tocopherol-stripped corn oil was used as the vehicle for BPA and DES, and was administered alone to control animals. No treatment-related effects on clinical observations, body weight, or food consumption were observed in adult females administered any dose of BPA or DES. Similarly, no treatment-related effects on growth or survival of offspring from dams treated with BPA or DES were observed. The total number of pups born per litter was slightly lower in the 200-microg/kg/day BPA group when compared to controls, but this change was not considered treatment-related since the litter size was within the normal range of historical controls. There were no treatment-related effects of BPA or DES on testes histopathology, daily sperm production, or sperm count, or on prostate, preputial gland, seminal vesicle, or epididymis weights at doses previously reported to affect these organs or at doses an order of magnitude higher or lower. In conclusion, under the conditions of this study, the effects of low doses of BPA reported by S. C. Nagel et al., 1997 (see above) and F. S. vom Saal et al., 1998 (see above), or of DES reported by F. S. vom Saal et al., 1997 (see above) were not observed. The absence of adverse findings in the offspring of dams treated orally with DES challenges the "low-dose hypothesis" of a special susceptibility of mammals exposed perinatally to ultra-low doses of even potent estrogenic chemicals. Based on the data in the present study and the considerable body of literature on effects of BPA at similar and much higher doses, BPA should not be considered as a selective reproductive or developmental toxicant.

Comparative activities of p-nonylphenol and diethylstilbestrol in noble rat mammary gland and uterotrophic assays.

Colerangle and Roy (1996, Endocrine 4, 115-122) have described the apparent ability of both diethylstilbestrol (DES) and p-nonylphenol (NP) to cause extensive cell proliferation and lobular development in the mammary glands of young adult Noble rats. The chemicals were administered over 11 days via subcutaneously implanted minipumps. The dose level of DES used (0.076 mg/kg/day) was about 70 times higher than its minimum detection level in rodent uterotrophic and reproductive toxicology studies. In contrast, the lowest active dose level of NP (0.073 mg/kg/day) in the Noble rat mammary gland study was about 600 times lower than its minimum detection level in rat uterotrophic and multigeneration studies. The apparent enhanced sensitivity of the Noble rat mammary gland to the estrogenic activity of NP was considered worthy of further study. Ovariectomized Noble rat uterotrophic assays with NP (minimum detection level approximately 40 mg/kg/day, 3 or 11 days, oral gavage) revealed similar assay sensitivity to that observed for earlier immature and ovariectomized Alderley Park (AP) rat uterotrophic assays of this chemical. The response of the ovariectomized Noble rat uterotrophic assay to DES and estradiol was also as expected from earlier immature AP rat assays. It is concluded that the general sensitivity to estrogens of the Noble rat and the AP rat is similar. A repeat of the Noble rat mammary gland study with DES (11 x 0.076 mg/kg/day) and NP (11 x either 0.073 or 53.2 mg/kg/day), as originally reported by Colerangle and Roy (1996), revealed a strong positive response to DES and no response to NP. It is concluded that the minimum detection level of NP as a weakly estrogenic material in the rat should be based on the results of rat uterotrophic and multigeneration studies and therefore be set at approximately 40 mg/kg/day. It is also concluded that induced S-phase in the rodent mammary gland is best monitored using BRDU, as opposed to PCNA staining, and that use of subcutaneously implanted minipumps/pellets is inappropriate for risk/hazard assessment studies of chemicals already established as estrogenic in vitro and in vivo, as are NP and DES.

Evaluation of compounds as barriers to dermal penetration of organophosphates using acetylcholinesterase inhibition.

An efficient, objective method for evaluating the efficacy of barrier compounds in preventing dermal penetration of organophosphates (OP) in rabbits was developed using time-dependent reduction in erythrocyte (RBC) acetylcholinesterase (AChE) activity as an endpoint. Anesthetized rabbits, with or without a dermal application of a mixture of high- and low-molecular-weight polyethylene glycols (mean molecular weight of 540 daltons; PEG 540), were exposed to different percutaneous doses of 3 highly toxic OP compounds. Dose-response curves were generated for RBC AChE inhibition as a function of percutaneous dose for each OP test material over time. From data generated, a single dose of each OP was selected to challenge PEG-540-protected and unprotected animals to validate the method as a means of differentiating effective from ineffective barriers to skin penetration. Data for a complete evaluation of a PEG 540 test barrier application were obtained within 4 h and anesthesia was maintained for the entire period.

Stagewise, adaptive dose allocation for quantal response dose-response studies.

A principal design objective of many dose-response studies is to estimate extreme percentiles of a dose-response distribution, e.g., the ED95 dose for a particular drug therapy, as precisely as feasible using the smallest number of experimental subjects possible. Such a design requirement necessitates that allocation of subjects to drug doses be carried out in a stagewise fashion to maximize the information obtained from each subsequent experimental observation in light of what has previously been determined. This paper describes and illustrates specialized methods and associated computer programs to evaluate, on a stagewise basis, the anticipated relative sensitivities of alternative experimental plans in the case of dichotomous responses. Following each stage of experimentation, the current estimates of the dose-response distribution parameters, as well as the uncertainties in these estimates, are updated and are used to assign subjects to experimental dose levels for the next stage of testing. Competing dose allocations are compared with respect to anticipated improvement in estimation precision. The adoption of such a stagewise dose allocation strategy is illustrated by example.

Stagewise, group sequential experimental designs for quantal responses. one-sample and two-sample comparisons.

The use of stagewise, group sequential experimental designs with dichotomous responses in toxicity or drug screening programs is discussed. Such designs represent a compromise between the standard, fixed sample size designs and fully sequential designs. Stagewise group sequential designs place specified numbers of animals on test at each stage, up to a maximum number of stages. The greatest increases in sample size efficiency occur with small numbers of stages, particularly when going from one stage to two. Two-stage designs can result in a 15 to 20 percent reduction in average sample size. Five-stage designs can result in a 30 to 40 percent reduction in average sample size, with no appreciable decrease in Type 1 error or power. Examples of the efficiencies that arose in actual screening programs are given. This paper demonstrates that the routine use of stagewise, group sequential designs in standardized screening protocols can result in substantial savings in animal use with virtually no sacrifice of statistical sensitivity.

Comparative immunotoxicity of 2,2'-dichlorodiethyl sulfide and cyclophosphamide: evaluation of L1210 tumor cell resistance, cell-mediated immunity, and humoral immunity.

The immunotoxicity of 2,2'-dichlorodiethyl sulfide (sulfur mustard, SM), on humoral and cell-mediated immunity was compared with that of the nitrogen mustard 2-[bis(2-chloroethyl)amino]tetrahydro-2H-1,3,2-oxazophosphorine 2-oxide (cyclophosphamide, CP). SM and CP had similar effects on thymic and splenic weights, spleen cell number, and the formation of antibody producing cells to sheep red blood cells (sRBC) when examined 5 days after exposure, but differed in their effects on body weights. Although there were no differences in the delayed hypersensitivity response to keyhole limpet hemocyanin, CP and SM had different effects in the L1210 tumor cell allograft rejection assay. CP, but not SM, decreased the 28 day survival rate of allogeneic mice exposed to a sublethal L1210 tumor challenge. The differing effects on survival to the L1210 tumor challenge could not be attributed to a direct cytotoxic effect of SM on the L1210 tumor cells as SM did not increase the survival rate or median survival time of syngeneic mice exposed to a lethal L1210 tumor cell challenge. In summary, SM and CP had immunosuppressive effects in the humoral immune assay. Although neither compound suppressed the delayed hypersensitivity response, CP was found to suppress host resistance to L1210 tumor cells.

Arsenic distribution in rabbits after Lewisite administration and treatment with British anti-Lewisite (BAL).

The standard treatment of Lewisite (dichloro(2-chlorovinyl)arsine) poisoning is by chelation with BAL (British anti-Lewisite, dimercaptopropanol). The present study investigated the effect of BAL treatment on the distribution of arsenic after Lewisite administration. Lewisite was administered subcutaneously at the LD10 and LD40 of the compound. Without BAL treatment arsenic was eliminated with a half-life in blood of between 55 and 75 hr and a blood clearance of 120 ml/hr/kg. Arsenic had a large volume of distribution of several liters per kilogram, indicating extensive distribution in tissues. The highest tissue concentrations, more than seven times blood concentrations, were found in the liver, lung, and kidneys. These organs maintained an approximately constant concentration ratio with blood during the sampling period. Concentrations in tissues with a blood-to-tissue barrier, such as the brain and the spinal cord, rose between 4 and 96 hr while blood concentrations declined more than fourfold over the same time period. BAL treatment by four equal, maximally tolerated doses over 12 hr substantially reduced arsenic concentrations in blood and tissues. For example, at 24 hr the concentrations in brain and liver (target organs for arsenic toxicity) were reduced by 65 to 89% over the range of Lewisite doses administered. The total exposure of brain and spinal cord was reduced by more than two-thirds by BAL treatment. Further, the blood clearance of arsenic was increased. BAL treatment enhanced the elimination of arsenic in two ways: by decreasing the tissue-to-blood partitioning which mobilizes arsenic into the blood stream, and by increasing the clearance of arsenic.