Structure and control of a cell-cell adhesion complex associated with spermiation in rat seminiferous epithelium.

Spermiation, the release of late spermatids from the Sertoli cell, is disrupted by a number of toxicants. Control of the spermiation process, and the proteins that interact to adhere mature spermatids to Sertoli cells, is poorly understood. In these studies we used immunohistochemistry, coimmunoprecipitation/Western blotting, and mass spectrometry to refine an earlier model of sperm adhesion proposed by our laboratory. We have identified specific proteins linked together as part of a multiprotein complex, as well as several additional proteins (cortactin, ERK1/2, and 14-3-3 zeta) that may be functioning in both structural and signal transduction roles. The current and prior data suggest that protein phosphorylation is central to the control of spermiation. We also present and characterize an in vitro tubule culture system that allowed functional testing of the spermiation model by pharmacologic manipulation, and yielded data consistent with the importance of protein phosphorylation in spermiation.

The effects of perinatal tebuconazole exposure on adult neurological, immunological, and reproductive function in rats.

Studies are under way to address concerns of potential persistent immunotoxic, reproductive, and neurotoxic effects of perinatal exposure to several pesticides. Tebuconazole, a triazole fungicide, was evaluated as part of this project. Sprague-Dawley dams were administered tebuconazole (0, 6, 20, or 60 mg/kg) by oral gavage daily from gestational day 14 to postnatal day (PND)7; the pups were then dosed daily at the same levels from PND7-42. Separate groups of rats were used for testing of immunological parameters, neurobehavioral testing using a screening battery of functional tests, and cognitive evaluations. Other groups of rats were evaluated for reproductive development and function, while yet others were sacrificed at the end of the dosing period for histological analyses of major organs systems, including neuropathological assessments. Pup viability and body weight were decreased in the highest dose group. There were no differences in the fertility indices in the exposed rats mated as adults. In the sheep RBC-immunized high-dose rats, spleen weights and cellularity were increased, and the ratio of cell types was altered compared to controls. There were, however, no biologically significant changes in the immune function of these rats. At necropsy on PND46 or 152, kidney, liver, and spleen weights were altered by tebuconazole treatment, but a dose-response relationship was not clear for most organs; only decreased kidney and increased liver weights were consistent in both sexes. Histological analyses were generally unremarkable outside of the brain. One month after the end of dosing, acquisition of learning the platform location in a water tank (i.e., Morris water maze) was impaired in the high-dose group; there were no differences in neuromuscular ability, motor activity, or swim speed to account for this finding. Furthermore, there was no effect on recall of the position during a free-swim trial. Neuropathological evaluations revealed pyknotic cells across hippocampal cell fields in animals of all tebuconazole treatment groups, with the highest incidence in the 20 and 60 mg/kg/day dose groups, coincident with cell loss within pyramidal cell layer of CA3-4 cell fields of the hippocampus and layer V of the neocortex. Thus, perinatal exposure to tebuconazole produced neurobehavioral deficits and neuropathology in rats, but did not alter immunological or reproductive function.

The effects of perinatal/juvenile heptachlor exposure on adult immune and reproductive system function in rats.

This study was performed to determine if developmental exposure of rats to heptachlor (H) during the last half of gestation through puberty adversely affects adult functioning of the immune and reproductive systems. Time-bred pregnant female Sprague-Dawley rats were dosed by gavage with H (0, 30, 300, or 3000 microg/kg/day) from gestation day (GD) 12 to postnatal day (PND) 7, followed by direct dosing of the pups with H through PND 42. Separate groups of rats were evaluated with a battery of immune function tests, while other groups of rats were evaluated for reproductive development and function. Additional groups of rats were euthanized at the end of the dosing period for histological analyses of major organ systems. Some dams and PND 7 pups were euthanized; milk, plasma, fat and/or tissues were assayed for H and heptachlor epoxide B (HEB), a major metabolite of H. The amount of H and HEB found in milk, blood, fat, and tissues was proportional to the dose of H administered. There were no effects on the number or survival of pups born to H-exposed dams nor to pups exposed postnatally. There were no effects on the number of treated dams delivering litters or on litter size, nor were there any effects on any of the reproductive end points examined in the F(0) or F(1) rats. There were no effects of H exposure on lymphoid organ weights, splenic natural killer (NK) cell activity, and splenic lymphoproliferative (LP) responses to mitogens and allogeneic cells in a mixed lymphocyte response (MLR) assay at 8 weeks of age. H exposure did not alter delayed or contact hypersensitivity at 10 or 17 weeks of age, respectively. However, the primary IgM antibody response to sheep red blood cells (SRBCs) was suppressed in a dose-dependent manner in males, but not females, at 8 weeks of age. The percentage of B lymphocytes (OX12(+)OX19(-)) in spleen was also reduced in the high-dose males. The anti-SRBC IgM response was reduced only in males exposed to 30 microg H/kg/day in a separate group of rats 21 weeks of age. In these same rats, at 26 weeks of age, the secondary IgG antibody response to SRBCs was suppressed in all of the H-exposed males, but not females. These data indicate that perinatal exposure of male rats to H results in suppression of the primary IgM and secondary IgG anti-SRBC responses. Suppression of these antibody responses persisted for up to 20 weeks after the last exposure to H, at a total exposure of approximately 1500 microg H/kg/rat.

Neurotoxicological outcomes of perinatal heptachlor exposure in the rat.

The developing nervous system has been identified as a potential target of pesticide exposure. Heptachlor is a cyclodiene pesticide that was widely used for many years, and for which inadvertent exposure to children and fetuses took place in the early 1980s; yet little is known regarding the developmental neurotoxicity of it and other cyclodienes. The aim of this study was to determine whether perinatal heptachlor exposure results in persistent alterations in nervous system function. Pregnant Sprague-Dawley dams were dosed from gestational day (GD) 12 to postnatal day (PND) 7, whereupon the rat pups were dosed directly until PND 21 (group A) or PND 42 (group B). Dose levels were 0, 0.03, 0.3, or 3 mg/kg/day, po. There were no dose-related effects on maternal weight, litter size, or pup growth. GABA(A) receptor binding (using [(35)S] tert-butylbicyclophosphorothionate; TBPS) and GABA-stimulated Cl- flux were evaluated in control and high-dose brain tissues taken on PND 7, 21, and 43. The B(max) values for [(35)S]-TBPS binding in brainstem, but not cortex, were decreased in female rats across all ages tested. There were no such changes in male rats, nor were K(D) values altered in either tissue or gender. GABA-stimulated Cl- flux was decreased in female cortex synaptoneurosomes only on PND 21. The ontogeny of the righting response (PND 2-5) was delayed in the high-dose females. All subsequent testing took place a week to months after dosing ceased. The functional observational battery (FOB) showed treatment-related, but not necessarily dose-related, changes in different aspects of the rat's reactivity and activity levels. Group-A rats also showed altered within-session habituation of motor activity. There were no heptachlor-related differences in motor activity following challenge with a range of chlordiazepoxide doses. Cognitive assessments were conducted in both groups of rats. There were no statistically significant differences among treatment groups in a one-trial passive avoidance test, although there was a trend toward less learning. In group B, rats (both sexes), heptachlor altered spatial learning in the Morris water maze during two weeks of daily training (2 trials/day). On probe trials, heptachlor-treated rats did not show significant preference for the correct quadrant (all dose groups in males, high dose in females). These rats did not show alterations on subsequent working-memory training (where the platform position was relearned each day). Thus, perinatal exposure to heptachlor produced neurochemical and persistent neurobehavioral changes, including alterations in spatial learning and memory.

The effects of perinatal/juvenile methoxychlor exposure on adult rat nervous, immune, and reproductive system function.

In order to address data gaps identified by the NAS report Pesticides in the Diets of Infants and Children, a study was performed using methoxychlor (MXC). Female rats were gavaged with MXC at 0, 5, 50, or 150 mg/kg/day for the week before and the week after birth, whereupon the pups were directly dosed with MXC from postnatal day (pnd) 7. Some dams were killed pnd7 and milk and plasma were assayed for MXC and metabolites. For one cohort of juveniles, treatment stopped at pnd21; a modified functional observational battery was used to assess neurobehavioral changes. Other cohorts of juveniles were dosed until pnd42 and evaluated for changes to the immune system and for reproductive toxicity. Dose-dependent amounts of MXC and metabolites were present in milk and plasma of dams and pups. The high dose of MXC reduced litter size by approximately 17%. Ano-genital distance was unchanged, although vaginal opening was accelerated in all treated groups, and male prepuce separation was delayed at the middle and high doses by 8 and 34 days, respectively. In the neurobehavioral evaluation, high-dose males were more excitable, but other changes were inconsistent and insubstantial. A decrease in the antibody plaque-forming cell response was seen in males only. Adult estrous cyclicity was disrupted at 50 and 150 MXC, doses which also showed reduced rates of pregnancy and delivery. Uterine weights (corrected for pregnancy) were reduced in all treated pregnant females. High-dose males impregnated fewer untreated females; epididymal sperm count and testis weight were reduced at the high, or top two, doses, respectively. All groups of treated females showed uterine dysplasias and less mammary alveolar development; estrous levels of follicle stimulating hormone were lower in all treated groups, and estrus progesterone levels were lower at 50 and 150 MXC, attributed to fewer corpora lutea secondary to ovulation defects. These data collectively show that the primary adult effects of early exposure to MXC are reproductive, show that 5 mg/kg/day is not a NO(A)EL in rats with this exposure paradigm (based on changes in day of vaginal opening, pubertal ovary weights, adult uterine and seminal vesicle weights, and female hormone data) and imply that the sites of action are both central and peripheral.

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.

Developmental toxicology: status of the field and contribution of the National Toxicology Program.

The NTP has conducted developmental toxicity studies on more than 50 chemicals, often in multiple species. Several chemicals caused developmental toxicity in the absence of any toxicity to the mother. Although hazard to humans is determined by the level of exposure to the chemical and its inherent toxicity, those agents that selectively disturb the development of the conceptus are of particular concern because other manifestations of toxicity would not warn the mother of overexposure. Whether the LOAEL (lowest-observed adverse effect level) for maternal toxicity was high or low did not correlate with the potential of chemicals to cause developmental toxicity. The form of developmental toxicity that determined the LOAEL most frequently was decreased body weight in mice and rats, but not rabbits, where the LOAEL was determined more often by an increase in resorptions. Several in vitro and short-term tests appear promising as screens to predict the outcome of developmental toxicity studies in mammals. However, the only screens that have undergone formal validation studies are those evaluated by the NTP. Improvements in our ability to predict risk to humans have been limited by our knowledge of the mechanisms by which agents cause developmental toxicity. Thus, future growth is dependent on a better understanding of the biological processes that regulate normal development, therein providing the necessary framework for understanding mechanisms of abnormal development.

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.

Limited PCB antagonism of TCDD-induced malformations in mice.

C57BL/6N mice used to model induction of cleft palate and kidney malformations in offspring following maternal treatment with TCDD, were dosed on gestation day (gd) 9 with 2,2',4,4',5,5'-hexachlorobiphenyl (HCB) (62.5, 125, 250, 500, 1000 mg/kg) and/or gd 10 with 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) (15 or 18 micrograms/kg) to investigate the potential protective effects of HCB against TCDD-induced teratogenicity. Maternal body weight gain was increased by combinations of 15 micrograms TCDD/kg and 125-500 mg HCB/kg and decreased at doses of 15 micrograms TCDD/kg + 1000 HCB mg/kg. At the doses used in this study, there was no effect of either compound on number of live or dead offspring. Fetal body weight was slightly decreased in all groups dosed with greater than or equal to 250 mg HCB/kg. HCB did not induce cleft palate at a dose of 1000 mg/kg, but did induce increases in hydronephrosis and hydroureter at 500 and 1000 mg/kg. Combinations of HCB and TCDD decreased the incidence of cleft palate induced by TCDD alone, but only at doses of 15 micrograms TCDD/kg combined with 125-500 mg HCB/kg. The antagonism of hydronephrosis (incidence and severity) appeared over a narrower dose range (15 micrograms TCDD/kg + 500 mg HCB/kg). HCB induced increases (3-fold) in ethoxyresorufin-O-deethylase (EROD) activity at doses of 500 and 1000 mg/kg, suggesting that the limited antagonism of TCDD teratogenicity by HCB could be under the control of the Ah-receptor.

Comparisons of the effects of TCDD and hydrocortisone on growth factor expression provide insight into their interaction in the embryonic mouse palate.

Cleft palate (CP) can be induced in embryonic mice by a wide range of compounds, including glucocorticoids and 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). Hydrocortisone (HC), a glucocorticoid, retards embryonic growth producing small palatal shelves, while TCDD exposure blocks the fusion of normally sized shelves. TCDD induction of CP involves altered differentiation of the medial epithelial cells. Recent studies indicate that growth factors such as EGF, TGF-alpha, TGF-beta 1, and TGF-beta 2 are involved in palatogenesis, regulating proliferation, differentiation, and extracellular matrix production. A synergism has been observed between HC and TCDD in which doses too low to induce CP alone are able to produce greater than 90% incidence when coadministered. In the present study a standard teratology protocol was performed in C57BL/6N mice to examine the synergism at doses lower than those previously published. Data from this study indicate synergistic interactions at doses as low as 3 micrograms TCDD/kg + 1 mg HC/kg. This extreme sensitivity suggests the involvement of a receptor-mediated mechanism possibly resulting in altered regulation of gene expression. Mechanisms of interaction were further studied by comparing growth of the shelves, fate of the medial epithelium, and expression of growth factor mRNAs and peptides. Pregnant mice were dosed on GDs 10-13 with HC (100 mg/kg sc) or with HC (25 mg/kg sc) + TCDD (3 micrograms/kg orally), doses producing 30% and 99% CP, respectively. The interaction between HC and TCDD results in a small HC-like palate, rather than the morphology typical of TCDD-induced clefting. Both compounds inhibited programmed cell death of the medial epithelium, which instead differentiated into an oral-like epithelium. The alterations in growth factor expression after HC or HC + TCDD were similar. Expression of EGF, TGF-beta 1, TGF-beta 2, and EGF receptor increased in specific palatal regions. Increased levels of mRNA were observed only for TGF-beta 1. The effect of TCDD alone on growth factor expression differ from those seen with HC or HC + TCDD. These divergent effects on growth factor expression may contribute to the differences in shelf size and thus to the different mechanisms of HC and TCDD clefting. Thus the synergism between HC and TCDD may involve similar and potentially additive effects on regulators of proliferation and differentiation in the palate, but additional contributing factors cannot be excluded.

Evaluation of the persistence of hydronephrosis induced in mice following in utero and/or lactational exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is an extremely potent teratogen in mice, inducing structural malformations in the kidney and secondary palate. Maternal depots of TCDD, stored primarily in adipose tissue, are mobilized during the nursing period. Thus, lactation serves as a significant route of exposure for the developing neonate. The objective of this present investigation was to assess whether hydronephrosis persisted postnatally, as well as to determine if the renal lesion could be induced lactationally. Pregnant C57BL/6N mice were treated once by gavage with 0, 3, or 12 micrograms TCDD/kg body wt on Gestation Day (GD) 6. All dams were allowed to litter, and each litter was standardized at random to a size of six pups. Standardized litters were then reciprocally cross-fostered on the day of birth. Postnatal Day (PND) 0, resulting in the establishment of four experimental groups: pups not exposed by either route, pups exposed only in utero, pups exposed only lactationally, and pups exposed by both routes. Pups were euthanized at one of two time points, either at weaning (PND 25) or at puberty (PND 67). TCDD was not overtly toxic to the dams or neonates with the dosing regime used in this study. Hydronephrotic incidence and severity, while greatest for pups receiving dual exposure, were essentially the same for pups exposed in utero only vs lactationally only. Lactational exposure induced hydronephrosis (HN), as well as exacerbated the severity of existing HN which was induced in utero. Regardless of the exposure group, the severity of the renal lesion was always greater in the right kidney than in the left. There were no sex-related differences in either the incidence or the severity of HN, nor was there any difference in response between PNDs 25 and 67. These data suggest that the renal lesion persists from weaning through puberty, despite the cessation of exposure. However, the data indicate that partial recovery from HN induced in utero occurs during the early postnatal period, as both hydronephrotic incidence and severity decreased with increasing age between GD 18 and PND 25. Recovery was most pronounced in the left kidney regardless of dose, thus suggesting that the ability to recover may in part be dependent upon the extent of renal damage.

Hydronephrosis in mice exposed to TCDD-contaminated breast milk: identification of the peak period of sensitivity and assessment of potential recovery.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is a potent inducer of hydronephrosis in both fetal and neonatal mice. A critical period of sensitivity to TCDD could not be identified for prenatally induced hydronephrosis since the urinary tract appeared equally sensitive throughout organogenesis. To identify the critical period of susceptibility for development of lactationally induced hydronephrosis in neonatal mice, as well as to characterize the potential for recovery from this renal lesion, dose-response and time-course studies were conducted in the postnatal period. Pregnant C57BL/6N mice were allowed natural delivery. In the dose-response phase of this investigation, mothers were administered 0, 3, 6, or 12 micrograms TCDD/kg once by gavage on Postnatal Day (PND) 1, 4, 8, or 14, and dams and pups were euthanized on PND 26. The kidneys were examined, and hydronephrotic severity was scored. The incidence and severity of hydronephrosis were significantly increased above controls only following treatment on PND 1 or 4, while on PND 8 the increase was marginal and pairwise tests were nonsignificant. Following treatment of dams on PND 1, the hydronephrotic response detected in 26-day-old pups was significantly greater than that for all later exposure days. In the time-course study, dams were given a single oral dose of 0 or 9 micrograms TCDD/kg on PND 1, and mothers and litters were subsequently euthanized on PND 7, 13, 19, or 26. Both hydronephrotic incidence and severity increased with time to euthanization following treatment on PND 1. Thus with the dosing regimen used in this study, recovery does not appear to occur between PNDs 7 and 26. Sex-related differences were observed, as the hydronephrotic response in males was generally greater than in females. In conclusion, the postnatal window of sensitivity during which TCDD can induce hydronephrosis is very narrow. Nonetheless, the hydronephrotic response induced during this early postnatal time is dramatic. Finally, PND 1 is the peak postnatal period of susceptibility for development of TCDD-induced hydronephrosis.

Teratogenic effects of 2,3,7,8-tetrabromodibenzo-p-dioxin and three polybrominated dibenzofurans in C57BL/6N mice.

Brominated flame retardants involved in many industrial uses contain polybrominated dibenzo-p-dioxins (PBDDs) and dibenzofurans (PBDFs) as contaminants. The levels of these contaminants can be dramatically increased by combustion. These chemicals are closely related in structure to the polychlorinated dibenzo-p-dioxins (PCDDs) and dibenzofurans (PCDFs), of which 2,3,7,8-tetrachloridibenzo-p-dioxin (TCDD) is the most toxic isomer. TCDD and related PCDFs are potent mouse teratogens inducing cleft palate and hydronephrosis at doses below those at which overt maternal and embryo/fetal toxicity occurs. This study examines the teratogenic effects of 2,3,7,8-tetrabromodibenzo-p-dioxin (TBDD), 2,3,7,8-tetrabromodibenzofuran (TBDF), 1,2,3,7,8-pentabromodibenzofuran (1PeBDF), and 2,3,4,7,8-pentabromodibenzofuran (4PeBDF) in C57BL/6N mice treated on gestation day (gd) 10 and examined on gd 18. Pregnant dams were treated with 0-4000 micrograms of each congener per kilogram body weight in 10 ml corn oil/kg. Dose selection was based on the relative toxicity of the chlorinated isomers. Maternal toxicity and developmental toxicity were assessed, and the hard palate and kidney, the target organs for the teratogenic effects of TCDD and related compounds, were examined for structural abnormalities. While the maternal liver weight increased at all dose levels examined for all four compounds, there was no evidence of any maternal toxicity. Embryo/fetal mortality was increased only at greater than or equal to 500 microgram TBDF/kg, while fetal weight increased in a dose-related manner following exposure to TBDD and TBDF. All compounds produced hydronephrosis (HN) at doses below that at which cleft palate (CP) occurred. The incidence of HN was significantly increased above background levels at the following doses (micrograms/kg): TBDD, 3; TBDF, 25; 1PeBDF, 500; 4PeBDF, 400. The LOELs (micrograms/kg) for CP were: TBDD, 48; TBDF, 200; 1PeBDF, 4000; 4PeBDF, 2400. The cleft palate incidence for all four brominated compounds and TCDD could be fit to a common slope, compatible with the concept that these chemicals all exert their teratogenic effects through a common mechanism. The potency of these chemicals, relative to TCDD as 1 for the induction of cleft palate, is TBDD, 0.24; TBDF, 0.10; 1PeBDF, 0.004; and 4PeBDF, 0.005. Previous studies from our laboratory had determined that the chlorinated dibenzofuran isomers had relative potencies of 0.05 (TCDF), 0.03 (1PeCDF), and 0.09 (4PeCDF). Thus, bromination decreases the teratogenic activity of TBDD relative to TCDD and of both 1- and 4PeBDF relative to the chlorinated isomers. However, substitution of bromines for chlorines increases the potency of TBDF relative to TCDF.(ABSTRACT TRUNCATED AT 400 WORDS)

Arsine: absence of developmental toxicity in rats and mice.

Arsine gas is a potent hemolytic agent but the effects of exposure to tolerated concentrations on pregnancy and prenatal development have not been reported. In the present evaluation, groups of bred mice and rats were exposed to arsine at concentrations of 0.025, 0.5, or 2.5 ppm on Gestation Days (gd) 6 through 15. Animals were killed on gd 17 (mice) or on gd 20 (rats) and endpoints of maternal and developmental toxicity were evaluated. In rats, maternal spleens were enlarged in the 2.5 ppm group and there was a decrease in packed red cell volume in pregnant rats. Fetuses weighed more than in the control group but other endpoints of developmental toxicity were not affected by arsine exposure. In another experiment involving separate groups of rats, the arsenic content of maternal blood and fetal livers increased with increasing atmospheric arsine concentrations, as assessed on gd 20. In mice, maternal spleen size was significantly increased in the 2.5 ppm group. The number of live fetuses, mean fetal body weight, and percentages of resorptions or malformations per litter were not affected by arsine exposure. In conclusion, arsine at atmospheric concentrations that caused increases in maternal spleen size and measurable levels of arsenic in maternal blood and fetal livers did not adversely affect endpoints of developmental toxicity.

Characterization of the peak period of sensitivity for the induction of hydronephrosis in C57BL/6N mice following exposure to 2,3,7, 8-tetrachlorodibenzo-p-dioxin.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is an extremely potent teratogen in mice. Hydronephrosis and cleft palate are the most sensitive measures of teratogenicity in mice following exposure to TCDD and other structurally related polyhalogenated aromatic hydrocarbons. Despite a relatively long half-life, investigators have identified a critical window for the induction of cleft palate in C57BL/6N mice. To characterize the critical period for renal teratogenesis, pregnant C57BL/6N mice were treated once by gavage with 0-24 micrograms TCDD/kg body wt on Gestation Day (GD) 6, 8, 10, 12, or 14. All dams were killed on GD 18, and the fetuses were examined for the presence of hydronephrosis and cleft palate. Maternal liver-to-body weight ratios were significantly elevated above controls on all days, while maternal weight gain was unaffected. Fetal mortality was increased relative to controls only at 24 micrograms TCDD/kg on GD 6. There was no significant difference in fetal body weights between control and TCDD-treated fetuses. The incidence of cleft palate increased in a dose-related fashion from GD 6 to GD 12, and identification of GD 12 as the critical window for induction of clefting of the hard palate was confirmed. Hydronephrosis was observed at all dose levels, regardless of exposure day, and the incidence was close to 100% at 3 micrograms TCDD/kg and higher doses on GD 12 and earlier. At all doses on GD 14, both the incidence and severity of hydronephrosis were decreased relative to all other days. There was a dose-related increase in the severity of the renal lesion on each day, but between GD 6 and 12 severity was constant. Thus, while palatal sensitivity to TCDD increased with gestational age between GD 6 and 12, there was no difference among these days in development of hydronephrosis. The data suggest, however, that on GD 14 the urinary tract may be less sensitive to TCDD.

Differential toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in C57BL/6J mice congenic at the Ah Locus.

The acute toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) was examined in male C57BL/6J mice differing only at the Ah locus. Wild type mice (Ahb/b, "b/b") were treated once with 0, 50, 100, 200, 300, and 400 micrograms TCDD/kg po while congenic mice (Ahd/d, "d/d") received a single dose of 0, 400, 800, 1600, 2400, and 3200 micrograms TCDD/kg. Mice were checked daily, weighed twice a week, and those that survived, killed 35 days post-treatment. The LD50 values were 159 and 3351 micrograms/kg for b/b and d/d mice, respectively. Mean time to death was 22 days and was independent of dose and genotype. Decrease in body weight gain was noted in both strains 5 days after treatment and occurred at doses greater than or equal to 100 micrograms/kg in b/b mice and 1600 micrograms/kg in d/d mice. Dose-related increases in liver weight (both absolute and relative to body weight) and decreases in thymus, spleen, testes, and epididymal fat pad weights were observed at 8-24-fold higher doses in d/d than in b/b mice. A dose-related increase in segmented neutrophils was observed in both strains. Serum chemistry values indicated that 8-24X greater doses of TCDD were needed to elevate sorbitol dehydrogenase, alanine aminotransferase, and 5'-nucleotidase and to decrease total and esterified cholesterol in d/d than in b/b mice. Few effects were seen on total bile acids, serum triglycerides, glucose, or nonesterified cholesterol. In the liver, hepatocellular cytomegaly, fatty change, and bile duct hyperplasia occurred in both strains in a dose-related manner, as did thymic and splenic atrophy. Necrosis of germinal epithelium in the testes and edema in the stomach submucosa occurred at acutely toxic doses. These lesions also occurred at doses 8-24X greater in d/d than in b/b mice. Thus, the spectrum of toxicity is independent of the allele at the Ah locus, but the relative dose needed to bring about various acute responses is approximately 8-24X greater in congenic mice homozygous for the "d" allele than for the wild type animals carrying two copies of the "b" gene.

Relative toxicity and tumor-promoting ability of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), 2,3,4,7,8-pentachlorodibenzofuran (PCDF), and 1,2,3,4,7,8-hexachlorodibenzofuran (HCDF) in hairless mice.

2,3,7,8-Tetrachlorodibenzo-p-dixoin 2,3,4,7,8-pentachlorodibenzofuran (PCDF), and 1,2,3,4,7,8-hexachlorodibenzofuran (HCDF) are highly toxic members of a class of environmental contaminants, the polychlorinated aromatic hydrocarbons (PCAH), which exhibit a similar and highly characteristic spectrum of toxic effects. For purposes of risk assessment, it is important to be able to make accurate estimates of the relative potency of these and related compounds. Previous investigations have indicated that, in acute exposure or in vitro studies, PCDF is approximately 0.1 times as toxic and HCDF is approximately 0.01 times as toxic as TCDD. In this study, we compared the relative toxicity and tumor-promoting abilities of TCDD, PCDF, and HCDF in hairless mouse skin. Female hairless mice (HRS/J hr/hr) were treated dermally with the initiator MNNG, then dosed twice weekly for 20 weeks with acetone, TCDD (2.5-10 ng/mouse/dose), PCDF (25-100 ng/mouse/dose), or HCDF (250-1000 ng/mouse/dose) as promoter. TCDD, PCDF, and HCDF were all potent promoters for the induction of squamous cell papillomas. There was, however, no difference in the incidence or multiplicity of papilloma formation between groups. The same doses of the three PCAH, in the absence of initiator, induced no skin papillomas. TCDD produced a significant increase in liver:body weight ratio (p less than 0.001) at all doses and a decrease in thymus:body weight ratio at a dose of 10 ng (p less than 0.001). Mice treated with PCDF and HCDF had marked thymic and splenic involution, liver hypertrophy, mucous cell hyperplasia in the fundic portion of the glandular stomach, and loss of body weight. PCDF and HCDF produced a greater incidence and severity of dermatotoxic effects than TCDD. Based on data for dermal toxicity and changes in body weight and organ weights, PCDF is estimated to be 0.2 to 0.4 times, and HCDF 0.08 to 0.16 times, as toxic as TCDD following repeated dermal exposure. Therefore, toxic equivalence factors generated using data from acute and/or in vitro studies may underestimate the risk from repeated low-dose exposures to these compounds.

Etiology of retinoic acid-induced cleft palate varies with the embryonic stage.

Retinoic acid (RA) has been shown to be teratogenic in many species, and 13-cis-RA is teratogenic in humans. Exposure to RA during embryonic morphogenesis produced a variety of malformations including limb defects and cleft palate. The type and severity of malformation depended on the stage of development exposed. The purpose of this study was to compare the effects of RA exposure in vivo on different stages of palate development. These results were compared to effects observed after exposure in organ culture. The vehicle used in RA dosing was also shown to be a major factor in the incidence of RA-induced cleft palate. For the in vivo studies, RA (100 mg/kg) in 10 ml corn oil/kg was given p.o. on gestation day (GD) 10 or 12, and the embryos were examined on GD 14 and 16. Exposure to RA in an oil:DMSO vehicle resulted in much higher incidences of cleft palate than were observed after dosing with RA in oil only. After exposure on GD 10, to RA, small palatal shelves formed which did not make contact and fuse on GD 14. The medial cells did not undergo programmed cell death. Instead, the medial cells differentiated into a stratified, squamous, oral-like epithelium. The RA-exposed medial cells did not incorporate 3H-TdR on GD 14 or 16, but the cells expressed EGF receptors and bound 125I-EGF. In contrast, RA-induced clefting after exposure on GD 12 did not involve growth inhibition. Shelves of normal size formed and made contact, but because of altered medial cell differentiation did not fuse. Medial cells differentiated into a pseudostratified, ciliated, nasal-like epithelium. This response was produced in vivo at exposure levels which produced cleft palate, and after exposure of palatal shelves to RA in vitro from GD 12-15. The medial cells exposed on GD 12 incorporated 3H-TdR on GD 14, expressed EGF receptors, and bound 125I-EGF. The responses to RA which lead to cleft palate differed after exposure on GD 10 or 12, and the pathways of differentiation which the medial cells followed depended on the developmental stage exposed.

Acute toxicity of perfluorodecanoic acid in C57BL/6 mice differs from 2,3,7,8-tetrachlorodibenzo-p-dioxin.

Perfluorodecanoic acid (PFDA) is a 10-carbon straight-chain fatty acid. Its toxicity in rats has been reported to resemble that produced by exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). Mice which are "responsive" to TCDD toxicity carry the Ahb allele, while mice homozygous for the Ahd gene are less sensitive to TCDD toxicity. To characterize the toxicity of PFDA and determine if it is under the control of the Ah locus, female responsive C57BL/6N (Ahb/b) mice and congenic C57BL/6J mice, differing only at the Ah locus (responsive, Ahb/b; heterozygous responsive, Ahb/d and "nonresponsive," Ahd/d), were administered a single oral dose of PFDA, at levels from 0 to 320 mg/kg body weight, observed daily for overt signs of toxicity, and weighed three times weekly. In the wild-type congenic C57BL/6J (Ahb/b) subline, mice were killed at 2, 7, 14, and 30 days following exposure. All other mice were killed on Day 30. Serum was taken from the C57BL/6N mice for analysis of thyroid hormone levels. Selected organs from all mice were weighed and fixed for histopathological examination. Dose-related mortality was observed as early as 5 days postexposure and time-to-death was inversely related to dose. Dramatic decreases in body weight occurred shortly following treatment in all strains. Serum triiodothyronine (T3) and thyroxine (T4) levels increased with increasing dose. There was a marked increase (p less than 0.05) in absolute and relative liver weights and a significant decrease in thymus weights. Hepatocellular hypertrophy was observed in all treated mice other than controls. A marked increase in hepatocyte peroxisomes was observed in all treatment groups. Thus, in contrast to TCDD, the acute toxicity of PFDA in the female C57BL/6 mouse does not vary with the Ah allele and is distinct from that reported for TCDD.

Retinoic acid and 2,3,7,8-tetrachlorodibenzo-p-dioxin selectively enhance teratogenesis in C57BL/6N mice.

TCDD is one of the most toxic man-made compounds and an extremely potent teratogen in mice. Many of its toxic symptoms resemble those seen during vitamin A deficiency. Vitamin A and its derivatives, such as alltrans-retinoic acid (RA), are also teratogenic in mice, as well as many other species. Both TCDD and RA produce cleft palate in susceptible strains of mice. However, while TCDD produces hydronephrosis, RA does not, and TCDD does not produce limb bud defects while RA does. To determine whether TCDD and RA would enhance or antagonize the teratogenic effects of the other compound, C57BL/6N dams were treated po on Gestation Day (gd) 10 or 12 with 10 ml corn oil/kg containing TCDD (0-18 micrograms/kg), RA (0-200 mg/kg), or combinations of the two chemicals. Dams were killed on gd 18 and toxicity and teratogenicity assessed. Coadministration of TCDD and RA had no effect on maternal or fetal toxicity beyond what would be expected by either compound alone. Cleft palate was induced by RA at lower doses on gd 10 than on gd 12, but by TCDD at lower doses on gd 12 than on gd 10. Sensitivity to TCDD-induced hydronephrosis was similar on both gd 10 and 12. The limb bud defects were only observed when RA was administered on gd 10, not when given on gd 12. No other soft tissue or skeletal malformations were related to administration of TCDD or RA. No effect of TCDD was observed on the incidence or severity of limb bud defects induced by RA, nor did RA influence the incidence or severity of hydronephrosis induced by TCDD. However, the incidence of cleft palate was dramatically enhanced by coadministration of the xenobiotic and vitamin. On both gd 10 and 12, the dose-response curves for cleft palate induction were parallel, suggesting some similarities in mechanism between the two compounds. However, combination treatment resulted in a synergistic response that varied with the stage of development and was tissue specific.