Changes in Androgen-Mediated Reproductive Development in Male Rat Offspring Following Exposure to a Single Oral Dose of Flutamide at Different Gestational Ages

Previous studies have indicated that the androgen receptor antagonist, flutamide, can produce a suite of reproductive malformations in the male rat when orally administered daily on gestation days (GD) 12-21. The objective of this study was to investigate the gestation time dependence for the induction of these malformations to establish a robust animal model for future studies of gene expression related to specific malformations. Groups of timed-pregnant Sprague-Dawley rats (GD 0 = day of mating) were administered flutamide as a single gavage dose (50 mg/kg) on GD 16, 17, 18, or 19 with 10 dams per group. Control animals (5 dams per time per group) were administered corn oil vehicle (2 ml/kg). Dams were allowed to litter, and their adult male offspring were killed at postnatal day (PND) 100 +/- 10. Anogenital distance was measured at PND 1 and 100. Areolae were scored at PND 13, and permanent nipples evaluated at PND 100. No reproductive tract malformations were found in control male offspring. In the treated groups, malformations were noted following exposure at every GD, although the incidence of specific malformations varied by GD. At GD 16, the highest incidence was noted for permanent nipples (46% pups, 60% litters), epispadias (12% pups, 30% litters), and missing epididymal components (5% pups, 20% litters). The highest incidences for hypospadias (58% pups, 80% litters), vaginal pouch (49% pups, 70% litters), cleft prepuce (29% pups, 60% litters), and missing prostate lobes (12% pups, 60% litters) were noted at GD 17. At GD 18 the highest incidence of malformations noted were epispadias (5% pups, 30% litters), reduced prostate size (32% pups, 90% litters), and abnormal kidneys (3% pups, 30% litters) and bladders (7% pups, 30% litters), while on GD 19 70% of the litters had animals with abnormal seminal vesicles. Testicular and epididymal morphological changes were noted at all GDs and were consistent with the gross observations and peaked in incidence and severity on GD17. The major discrepancy between this study and previous multiple-dose studies was in the very few numbers of animals presenting with cryptorchidism (only one each on GDs 16 and 17), suggesting that exposure over multiple days may be required to induce this malformation. Thus, a single gestational exposure of flutamide induced numerous reproductive tract malformations consistent with previously reports following multiple exposures, with the timing of the exposure producing marked tissue selectivity in the response noted in adult offspring.

Mercury concentrations in brain and kidney following ethylmercury, methylmercury and Thimerosal administration to neonatal mice

The distribution of mercury to the brain following an injection of methylmercury (MeHg) or ethylmercury (EtHg) was examined in immature mice. Postnatal day (PND) 16 CD1 mice received MeHg chloride either by IM injection or by gavage. At 24 h and 7 days post-injection, total mercury concentrations were determined in blood, kidney, brain, and muscle by cold vapor atomic fluorescence spectrometry. At 24 h, an IM injection of MeHg chloride (17.4 microg) produced total mercury concentrations in the blood (6.2 +/- 0.9 microg/g), brain (5.6 +/- 1.3 microg; 0.6% delivered dose), and kidney (25.2 +/- 5.6 microg; 1.1%), approximately 30% of that obtained from oral administration (blood: 17.9 +/- 1.0 microg; brain: 16.1 +/- 1.2 microg, 1.5%; kidney: 64.9 +/- 6.3 microg, 2.7%). For comparison, PND 16 mice received an IM injection of concentrated dosing suspensions (2 microl dosing vol.) for EtHg chloride (6 microg) or Thimerosal (15.4 microg). For EtHg, approximately 0.39 +/- 0.06% of the injected mercury was detected in the brain and 3.5 +/- 0.6% in the kidney at 24 h. Thimerosal IM injection resulted in 0.22 +/- 0.04% in the brain, and 1.7 +/- 0.3% in the kidney. By 7 days, mercury levels decreased in the blood but were unchanged in the brain. An acute IM injection to adult mice of each suspension at a 10-fold higher dose resulted an average 0.1% mercury in the brain, and higher levels in the blood, kidney, and muscle as compared to the young. In immature mice, MeHg delivered via oral route of administration resulted in significantly greater tissue levels as compared to levels from IM injection. Comparisons of tissue distribution following IM administration suggest that an oral route of administration for mercury is not comparable to an IM delivery and that MeHg does not appear to be a good model for EtHg-containing compounds.

Cadmium at a non-toxic dose alters gene expression in mouse testes

The testes are important targets of cadmium (Cd)-induced toxicity and carcinogenicity in rodents. Exposure to Cd at environmentally relevant low levels is a significant human health concern, but the effects of Cd on the rodent testes at doses that do not cause overt lesions are poorly defined. We used cDNA microarray and quantitative real-time RT-PCR assays to determine gene expression profiles in the testes of CD-1 mice 12-72 h after a single s.c. injection of 5 micromol/kg CdCl2. This dose of Cd did not produce overt histopathological changes, but clearly altered the expression of some genes that are likely to be important in toxicity responses. The most significant changes in gene expression occurred 24 h after treatment, corresponding to when the highest level of Cd was detected in the testes. Increased expression of the C-myc and Egr1 genes strongly suggests acute stress responses. Repressed expression of cell cycle-regulated cyclin B1 and CDC2 proteins indicates a potential for causing G2/M arrest and disturbance of meiosis. Decreased expression of pro-apoptotic genes, particularly Casp3, and DNA repair genes possibly contributes to Cd-induced carcinogenesis. These results indicate that changes in gene expression occur well before overt effects of Cd-induced testicular toxicity and carcinogenicity are apparent.

Effects of boric acid supplementation on bone histomorphometry, metabolism, and biomechanical properties in aged female F-344 rats

Postmenopausal women may benefit from dietary interventions in order to increase bone strength and prevent fractures. Dietary boron (B) may be beneficial for optimal calcium metabolism and, as a consequence, optimal bone metabolism. The present study evaluated the effects of boron, in the form of boric acid, with or without 17beta-estradiol (E2) supplementation (via subcutaneous implant), in ovariectomized (OVX) aged 13- mo-old F-344 rats. Boric acid was administered by gavage at a subtoxic dose (8.7 mg B/kg/d) for 40 d. Results indicate that serum level of minerals as well as osteocalcin (a marker of bone resorption) are dependent to a greater extent on the hormonal status of the animals than on boron supplementation. Boron treatment increased the E2-induced elevation of urinary calcium and magnesium. Bone mineral density (BMD) of the L5 vertebra and proximal femur was highest in the E2-treated groups; no increase in BMD was conferred by boron treatment. By histomorphometry of the proximal tibial metaphysis, osteoblastic, osteoid, and eroded surfaces were significantly suppressed by E2 treatment, but not by boron treatment. In biomechanical testing of femur and vertebra, neither E2 nor boron treatment significantly increased bone strength. At the levels given, boron alone provided no protection against OVX-induced osteopenia. In addition, combination therapy (B + E2) provided no additional benefits over those of 17beta-estradiol treatment alone in this aged rat model.

The pesticide methoxychlor given orally during the perinatal/juvenile period, reduced the spermatogenic potential of males as adults by reducing their Sertoli cell number

Perinatal and juvenile oral treatment of rats with the insecticide, methoxychlor (MXC), reduced testicular size and other reproductive indices including the number of epididymal spermatozoa in those animals as adults 161. The objective was to determine if these males exposed during development had fewer Sertoli cells which might explain these testicular effects. Rat dams were gavaged with MXC at 0, 5, 50, or 150 mg x kg(-1) x day(-1) for the week before and after they gave birth. Resulting male pups (15/group) then were dosed directly from postnatal day 7 to 42. Testes were fixed in Bouin's and in OsO4, embedded in Epon and sectioned at 0.5 microm, stained with toluidine blue, and evaluated stereologically or cut at 20 microm to measure Sertoli cell nuclei with Nomarski optics. Sertoli cell number was calculated as the volume density of the nucleus times the parenchymal weight (90% of testicular weight) divided by the volume of a single Sertoli cell nucleus. Across dose groups, there were no changes in the nuclear volume density, the volume of a single nucleus, or the number of Sertoli cells per g parenchyma. There were highly significant dose-related changes in the volume of Sertoli cell nuclei per testis and the number of Sertoli cells per testis. Reduced testicular weight (r = 0.94) and reduced numbers of epididymal spermatozoa (r = 0.43) were significantly (p < 0.01) correlated to reduced number of Sertoli cells per testis. Hence, perinatal and juvenile oral exposure to MXC can reduce spermatogenic potential of males as adults by reducing their number of Sertoli cells.

The hidden effect of estrogenic/antiandrogenic methoxychlor on spermatogenesis

Perinatal and juvenile oral treatment of rats with methoxychlor (MXC) only during development reduces testicular size and Sertoli cell number in those animals as adults. The objectives were to determine if MXC administered orally reduces numbers of spermatogonia and daily sperm production that parallel reduction in Sertoli cell number and if germ cell degeneration rate or function of individual Sertoli cells was also affected. Rat dams were gavaged with MXC at 0, 5, 50, or 150 mg/kg/day for the week before and after they gave birth. Resulting male pups (14-16 per group) then were dosed directly from postnatal day 7 to 42. Testes were fixed in Bouin's fixative, postfixed in osmium tetroxide, and embedded in Epon. Sections of 0.5 and 20 microm were evaluated stereologically. Across dose groups, body weight was not affected, but testicular weight was significantly reduced in a dose-dependent fashion. Spermatogenic potential based on number of spermatogonia and number of spermatids per testis was significantly reduced by treatment. There was no adverse effect on daily sperm production per gram of parenchyma based on spermatids; however, the number of spermatogonia per gram was reduced. The ratio of spermatid number per spermatogonia was higher in the MXC-treated groups. This difference indicated that the testis can compensate for the treatment-induced reduction in number of spermatogonia by reducing degeneration of their progeny. However, the reduced number of Sertoli cells prevented the compensation from recovering the daily sperm production per testis totally. Given that endocrine disruptors like MXC can induce compensation during spermatogenesis, it may reduce the ability of the testis to compensate during subsequent exposures.

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.

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.

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.

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.

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.

Developmental toxicity of perfluorodecanoic acid in C57BL/6N mice

Perfluorodecanoic acid (PFDA) is a representative of the perfluorinated carboxylic acids used as commercial wetting agents and flame retardants. Signs of PFDA toxicity have been reported to resemble those seen after exposure to TCDD. To determine if PFDA exhibits teratogenic effects similar to those of TCDD or is a developmental toxin, time-mated C57BL/6N mice were administered PFDA by gavage in corn oil (10 ml/kg) on gestation days (gd) 10-13 or gd 6-15 at levels of 0, 0.25, 0.5, 1.0, 2.0, 4.0, 8.0, 16.0, or 32.0 mg/kg/day or 0, 0.03, 0.3, 1.0, 3.0, 6.4, or 12.8 mg/kg/day, respectively. Dams were killed on gd 18 and maternal and fetal toxicity was assessed. Fetuses were examined for external, visceral, or skeletal malformations. Maternal body weight gain (corrected for the weight of the gravid uterus) was significantly reduced as a result of PFDA treatment at 6.4 and 12.8 mg/kg/day (gd 6-15) and 16.0 and 32.0 mg/kg/day (gd 10-13). Fetal viability was decreased only in those groups showing extensive maternal body weight loss. Fetal body weights were significantly reduced at levels as low as 0.1 mg/kg/day (gd 6-15) and 0.5 mg/kg/day (gd 10-13). No hydronephrosis, cleft palate, or edema was observed nor were any other soft tissue or skeletal malformations detected. Thus, PFDA does not produce malformations in C57BL/6N mice, and the developmental toxicity observed (increased fetal mortality and decreased live fetal body weight) was seen only at doses that were maternally toxic.

Developmental toxicity of 2,3,4,7,8-pentachlorodibenzofuran in the Fischer 344 rat

Fischer 344 rats were exposed acutely to 2,3,4,7,8-pentachlorodibenzofuran (4-PeCDF) during the organogenic period to evaluate its potential as an inducer of teratogenic and embryolethal effects. All dams were treated by gavage with a single dose of 0, 30, 100, or 300 micrograms 4-PeCDF/kg body wt on gestation Day (gd) 8, 10, or 12. An additional treatment group was included on gd 12 and administered 10 micrograms 4-PeCDF/kg body wt po. All animals were killed on gd 20 and maternal and fetal toxicities were assessed. Determination of embryotoxicity involved both soft tissue and skeletal examinations. 4-PeCDF induced a dose-related decrease in corrected maternal weight gain following treatment on gd 8 and 10, as well as resulted in a concomitant increase in the liver/body weight ratios, first evident at 30 micrograms/kg for all 3 days of exposure. The maternal thymus weight decreased relative to body weight compared with those of controls. Embryo-fetal toxicity was evident from the high mortality (greater than 80%) observed at 300 micrograms/kg for all 3 days of exposure. Mean fetal weight, a sensitive indicator of fetal toxicity, decreased compared to that of controls at 30, 100, and 300 micrograms/kg following treatment on either gd 8, 10, or 12.4-PeCDF induced cleft palate in survivors at a dose of 300 micrograms/kg for all 3 days of exposure. In conclusion, 4-PeCDF is maternally and fetally toxic regardless of the gestation day of exposure, but induced terata only at doses where overt maternal and fetal toxicity were observed, in contrast to previously reported studies in the mice where teratogenic effects were observed at nonfetotoxic dose levels. Thus, the mouse may be a more sensitive model for evaluating specific toxic responses induced prenatally following exposure to the structurally related polyhalogenated aromatic hydrocarbons which include the dioxins, furans, biphenyls, and naphthalenes.

Developmental toxicity screen: results of rat studies with diethylhexyl phthalate and ethylene glycol monomethyl ether

The purpose of these investigations was to develop a protocol for an in vivo developmental toxicity screen (DETS) that would provide sufficient data to determine whether to 1) do a full developmental toxicity evaluation without additional range-finding studies, or, depending on the results, to 2) do no further testing of a chemical. In order to evaluate this screen, we compared results obtained by using the DETS protocol with results of previously conducted developmental toxicity evaluations of diethylhexyl phthalate (DEHP) and ethylene glycol monomethylether (EGME). Five groups (n greater than or equal to 17) of F344 rats were treated on days 6-15 of gestation by dosed feed (DEHP levels = 0, 0.5, 1.0, 1.5, 2.0%) or gavage (EGME doses = 0, 12.5, 25, 50, 100 mg/kg/day). One half of the rats in these studies were killed on day 16 of gestation, and the remaining animals were allowed to deliver litters which were killed on day 4. EGME caused only a small decrease in maternal weight gain during treatment (100 mg/kg group) that was accompanied by a decrease in gravid uterine weight. The percentage of resorptions was increased in the 50 and 100 mg/kg groups. The number of live pups was decreased in the 25, 50, and 100 mg/kg groups, and litter weight and postnatal survival were decreased in the 100 mg/kg group. These results are consistent with those reported in developmental toxicity studies on EGME conducted by the inhalation and dermal routes. With DEHP, there were treatment-related reductions in maternal body weight and weight gain. There was also a nonstatistical increase in percentage of resorptions per litter that was also observed, but at relatively high levels, in a definitive study in which F344 dams were treated on days 0-20 of gestation. The results of studies on these two chemicals compare well with published results and would have led to the selection of proper dose levels for subsequent FDA segment 2 studies.

Testicular toxicity and reduced Sertoli cell numbers in neonatal rats by di(2-ethylhexyl)phthalate and the recovery of fertility as adults

Neonatal and adult rats (1, 2, 3, 6, and 12 weeks of age) were given five daily oral doses of di(2-ethylhexyl) phthalate (DEHP) (0, 10, 100, 1000, 2000 mg/kg) and histological changes in the testes were examined 24 hr after the last dose. Relative testis weights were reduced at doses of 1000 mg/kg in 1, 2, 3, and 6-week-old but not in 12-week-old rats, while doses of 2000 mg/kg were fatal to suckling rats and caused decreased relative testis weight but not death in 6- and 12-week-old rats. In neonatal rats (1 week old), DEHP (1000 mg/kg) caused a 35% decrease in Sertoli cell numbers while 2- and 3-week-old rats showed losses of spermatocytes but not of Sertoli cells. The 6- and 12-week-old rats showed loss of both spermatids and spermatocytes at 1000 and/or 2000 mg/kg. Total testicular zinc concentrations were decreased in 12-week-old but not in suckling (3-week) or weaned (6-week) rats. The results support the hypothesis that the Sertoli cell is the primary testicular target of phthalate ester toxicity since effects were observed at an age when only Sertoli cells were present. Fertility was assessed in mating trials in adult male rats after neonatal exposure to DEHP on Days 6-10. Although Sertoli cell number was reduced 24 hr after the last dose, the numbers were normal at 6 and 13 weeks of age. However, at 6 weeks there was a dose-related decrease in maturation of the spermatids in the tubules. There were no consistent changes in fertility, implantation rate, or numbers of live fetuses in untreated females mated with the DEHP-treated males. However, there were decreases in testis weight and testicular spermatid numbers at 13 and 19 weeks but not at 11, 12, 16, or 23 weeks of age. Therefore, a loss of Sertoli cells due to DEHP exposure neonatally did not affect the fertility of the rats as adults, but may have caused subtle effects on sperm production.

Teratogenic effects of polychlorinated dibenzofurans in combination in C57BL/6N mice

Polychlorinated dibenzofurans (PCDFs) are highly toxic environmental contaminants which have been involved in several incidents of human poisoning. Two congeners, 2,3,4,7,8-pentachlorodibenzofuran (4-PeCDF) and 1,2,3,4,7,8-hexachlorodibenzofuran (HCDF), have been shown to persist in the tissues of victims of accidental ingestion from Japan and Taiwan. The teratogenicity of these compounds, both alone and in combination, was assessed in C57BL/6N mice. Pregnant mice were treated with 10 ml/kg corn oil containing no PCDFs, 4-PeCDF (0-30 micrograms/kg), HCDF (0-300 micrograms/kg), or a combination of the two on gestation Days 10-13, followed by necropsy on gestation Day 18. Maternal and fetal toxicity were assessed and selected soft tissues were examined for abnormalities. Both chemicals caused hydronephrosis and cleft palate in the absence of any overt toxicity. Hydronephrosis occurred at doses approximately fivefold lower than those causing cleft palate. The combination of 4-PeCDF and HCDF was additive for terata based on responses predicted by probit analysis. In addition, the combination of 2,3,4,5,3',4'-hexachlorobiphenyl (0-60 mg/kg), a structurally related compound also present in PCDF poisoning victims, and 4-PeCDF appears additive. Thus, these chemicals, which cause toxic effects similar to those of 2,3,7,8-tetrachlorodibenzo-p-dioxin, are additive in the induction of fetal anomalies in the mouse.

Teratogenicity of three polychlorinated dibenzofurans in C57BL/6N mice

Polychlorinated dibenzofurans (PCDFs) are widespread environmental contaminants which have been detected in human tissues and implicated in several poisoning incidents. Their toxic effects are similar to those observed with other related halogenated aromatic hydrocarbons such as TCDD. The teratogenic effects of three PCDFs, 1,2,3,7,8-pentachlorodibenzofuran (1-PeCDF), 2,3,4,7,8-pentachlorodibenzofuran (4-PeCDF), and 1,2,3,4,7,8-hexachlorodibenzofuran (HCDF), were assessed in C57BL/6N mice. Pregnant mice were exposed on Gestation Days 10-13 to 10 ml corn oil/kg containing PCDFs. The dams were killed on Gestation Day 18 and maternal and fetal toxicity were assessed. All three compounds were highly teratogenic, with very steep and parallel dose-response curves for the two diagnostic indicators of dioxin-like teratogenicity, hydronephrosis, and cleft palate. 4-PeCDF was the most teratogenic with an ED50 of 36 micrograms/kg for cleft palate and 7 micrograms/kg for hydronephrosis. 4-PeCDF was approximately 4 times as potent as 1-PeCDF and 10 times as potent as HCDF. The teratogenic responses occurred at a dose below that where any obvious maternal or fetal toxicity was detected. Thus, these three compounds cause teratogenic responses similar to those seen with TCDD but are only 1/10 to 1/100 as potent.

Reproductive toxicology of methyldopa in male F344/N rats

Methyldopa, a widely used antihypertensive drug, was administered to male Fischer 344/N rats by gavage 5 days/week for 65 days at dosages of 0, 50, 100, 200, or 400 mg/kg. Decreased body weight was seen in treated animals. After mating to untreated female Fischer 344/N rats on days 57-61, the male rats were necropsied (days 65-67) and reproductive toxicity was measured by sperm count, sperm motility, organ weights, hormone levels and histologic evaluation of the testis. Decreased fertility was seen in males dosed with 200 or 400 mg/kg methyldopa. Decreases were also seen in sperm count, sperm motility, apparent number of late spermatids, and plasma testosterone levels in males in the 200 and 400 mg/kg groups. This alternation of reproductive function in male rats was found to be reversible after a 13-week recovery period without dosing. The marked decrease in circulating testosterone levels following methyldopa treatment at 200 or 400 mg/kg may have contributed to the reproductive toxicity of this drug.

Effects of thyroid hormones on the induction of cleft palate by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in C57BL/6N mice

The induction of cleft palate by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) administered with thyroid hormones triiodothyronine (T3) or thyroxine (T4) was investigated in C57BL/6N mice. Timed-pregnant mice were treated with vehicle, TCDD, T3, T4, TCDD plus T3, or TCDD plus T4 on Days 10 to 13 of gestation. No cleft palates were observed in any control fetuses in this study, nor have there been any cleft palates in 1193 fetuses or 154 control litters in the past 24 months. TCDD (3 micrograms/kg/day) caused about 8% cleft palates per litter, while T3 (120, 240, 480 micrograms/kg/day) and T4 (625, 1250, 2500 micrograms/kg/day) resulted in no more than 1.2% cleft palates per litter in any of the treatment groups and the incidence was not dose related. The combination of TCDD (3 micrograms/kg/day) plus T3 at 120, 240, and 480 micrograms/kg/day resulted in 15.9, 20.6, and 31.4% cleft palates per litter, respectively. TCDD plus T4 at 625, 1250 and 2500 micrograms/kg/day caused 15.1, 22.9, and 27.2% cleft palates per litter. No cleft palates were observed when large doses of T3 were given in combination with T4. These data demonstrated that coadministration of T3 or T4 with TCDD increased the incidence of cleft palate to incidences greater than expected from the separate administration of the hormones plus TCDD.

Effect of anterior hypothalamic deafferentation and continuous growth hormone infusion on the hepatic synthesis of alpha 2u-globulin in the male rat

Anterior hypothalamic deafferentation and infusion of human GH (hGH) in the normal male rat caused a marked reduction in the hepatic concentration of alpha 2u-globulin, an androgen-dependent protein. Although s.c. injections of hGH (twice-daily) resulted in more than a 50% reduction in the hepatic level of alpha 2u-globulin, the same dose of hGH when administered continuously through osmotic minipumps caused a threefold greater inhibition. The decreased hepatic concentration of alpha 2u-globulin after hGH administration was associated with corresponding changes in the hepatic level of translatable alpha 2u-globulin messenger RNA. Continuous infusion of hGH through osmotic minipumps and removal of the anterior hypothalamic influence on GH secretion by deafferentation also caused a marked reduction in the cytoplasmic androgen-binding activity of the rat liver. These results suggest that alterations in the level and pattern of GH secretion may influence hepatic androgen-binding activity and alpha 2u-globulin synthesis.

Synergistic interaction of 2,3,7,8,-tetrachlorodibenzo-p-dioxin and hydrocortisone in the induction of cleft palate in mice

Glucocorticoids cause cleft palate in sensitive mouse strains by interfering with the proliferation of mesenchymal cells in the palatal shelves; 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) also causes cleft palate, but its effects involve the epithelial cells. The purpose of this study was to examine the interaction of TCDD and the glucocorticoid hydrocortisone in the induction of malformations. Pregnant C57BL/6N mice were treated on gestation days 10-13 with TCDD (0 or 3 micrograms/kg, p.o.), hydrocortisone (0, 25, 50, or 100 mg/kg, s.c.) or a combination of TCDD and hydrocortisone. The dams were killed on gestation day 18 and the mice were analyzed for maternal and fetal toxicity and soft tissue malformations. TCDD alone had no effect on litter size, fetal weight or viability, or maternal weight gain. This dose of TCDD is essentially a threshold dose and it did not produce cleft palate in this study, but all the TCDD-treated fetuses had hydronephrosis, the most sensitive indicator of TCDD teratogenicity. Hydrocortisone alone caused dose-related decreases in fetal weight and maternal liver/body weight ratios, and dose-related increases in cleft palate (0, 5, 10, and 30%). No effects of hydrocortisone were detected on litter size or fetal viability, but maternal weights were affected. Combination of all doses of hydrocortisone with TCDD resulted in a 100% incidence of cleft palate, accompanied by a decrease in litter size and fetal weight and an increase in fetal mortality related to the dose of hydrocortisone. TCDD tended to reverse the decrease in liver/body weight ratio seen with hydrocortisone alone.(ABSTRACT TRUNCATED AT 250 WORDS)

Teratogenic potency of TCDD, TCDF and TCDD-TCDF combinations in C57BL/6N mice

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) and 2,3,7,8-tetrachlorodibenzofuran (TCDF) cause the same spectrum of fetal anomalies in C57BL/6N mice. Pregnant dams were treated with TCDD, TCDF and combinations of the 2 compounds on gestation day 10, and examined for maternal and fetal effects on day 18. The fetal kidneys were the most sensitive target for teratogenicity. The dose response for cleft palate induction fit the probit model for both compounds, suggesting that TCDD was approximately 30 times more potent than TCDF. The interaction between these 2 compounds was consistent with a model for additive toxicity.

Toxic interaction of specific polychlorinated biphenyls and 2,3,7,8-tetrachlorodibenzo-p-dioxin: increased incidence of cleft palate in mice

The induction of cleft palate in C57BL/6N mice is an extremely reproducible and sensitive indicator of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) toxicity. This endpoint was used to look for potential interactions between two polychlorinated biphenyl (PCB) congeners and TCDD. Both 2,3,4,5,3',4'-hexachlorobiphenyl (HCB) and 2,4,5,2',4',5'-HCB are of relatively low toxic potency, but their biological properties differ. Pregnant mice were treated with TCDD and either HCB on gestation Days 10 through 13, and the fetuses examined for the presence of cleft palate and renal abnormalities on gestation Day 18. At a dose of TCDD which caused a low level of cleft palate, moderate hydronephrosis was observed. No renal or palatal anomalies were detected after 2,4,5,2',4',5'-HCB treatment, and the combination of this isomer with TCDD had no effect on the incidence of TCDD-induced cleft palate. 2,3,4,5,3',4'-HCB caused mild renal toxicity, but no cleft palate. However, treatment of pregnant mice with a combination of TCDD and 2,3,4,5,3',4'-HCB resulted in a 10-fold increase in the incidence of cleft palate. Thus, the toxicity of compounds such as TCDD may be enhanced by compounds of relatively low acute toxicity such as selected PCBs. The widespread environmental occurrence of such combinations suggests a need for further evaluation of the mechanism of this interaction.

Dimethyl methyl phosphonate induction of dominant lethal mutations in male mice

The reproductive toxicity of dimethyl methyl phosphonate (DMMP) was studied in the male B6C3F1 mouse. Male mice were treated with 0, 250, 500, 1000, and 2000 mg/kg DMMP by gavage 5 days per week for 13 weeks. After 4, 8 and 12 weeks of treatment the male mice were mated to untreated CD-1 female mice. At the two highest doses (1000 and 2000 mg/kg) the chemical caused a dominant lethal effect (early resorptions). Groups of male mice (at 1000 and 2000 mg/kg), mated after a 15-week recovery period without chemical dosing, had a resorption rate comparable to the control group. After 13 weeks of dosing, the male mice showed no histopathologic changes of the reproductive organs, no abnormalities in sperm concentration or sperm morphology, no evidence for hormone imbalance, no signs of general toxicity, and no effects on the fertilization rate. The male B6C3F1 mouse was less responsive than the male Fischer 344/N rat to the reproductive toxic effects of DMMP.

Reproductive toxicity of dimethyl methyl phosphonate (DMMP) in the male Fischer 344 rat

Dimethyl methyl phosphonate (DMMP) has been considered for use by the U.S. Armed Forces as a nerve gas simulant in a variety of experimental situations to simulate the physical properties of nerve gases, but not the neurotoxic properties. Dimethyl methyl phosphonate is also used as a flame retardant for urethane foams and polyester resins. This study was conducted to determine the reproductive toxicity of DMMP after subchronic dosing. DMMP was administered to male Fischer 344 rats by gavage 5 days/week for 90 days at dosages of 0, 250, 500, 1000, and 2000 mg/kg, and all animals survived this dosing schedule. At Day 84, the rats were mated to untreated female Fischer 344 rats. There was a dose-related decrease in sperm count, sperm motility, and the male fertility index. The male fertility index was 70, 75, 60, 40, and 0% in the 0, 250, 500, 1000, and 2000 mg/kg dose groups. DMMP acted as a dominant lethal mutagen as demonstrated by an increase in the number of resorptions with increasing doses of the drug. The percentage of resorptions in the control group was 6.1% and increased to 14.9, 37.8, and 79.1% in the 250, 500, and 1000 mg/kg groups, respectively. The testes of the male rats were examined histologically to determine the relationship between reproductive function and pathologic abnormalities. DMMP altered reproductive function at all dose levels, while histologic abnormalities of the testis were seen only in the high-dose group. Changes in the testes of the high-dose animals were characterized by lack of spermatogenesis or by degeneration, vacuolization, and necrosis of cells in the spermatogenic tubules. Histopathologic abnormalities of the kidney were seen in some animals from each of the dosed groups and microscopic changes of the prostate were seen in some of the high-dose animals.

Dioxin in soil: bioavailability after ingestion by rats and guinea pigs

Soil environmentally contaminated with 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) was given by gavage to guinea pigs and rats. The development of a characteristic clinicopathologic syndrome in guinea pigs, the induction of aryl hydrocarbon hydroxylase in rats, and the presence of TCDD in the livers of both species show that TCDD in soil exhibits high biological availability after ingestion.

Teratogenicity of 2.3.7.8-tetrachlorodibenzofuran (TCDF) in mice

Treatment of pregnant C57BL/6N mice with 2,3,7,8-tetrachlorodibenzofuran (TCDF) (0, 250, 500, and 1000 micrograms/kg on gestation day 10 or 0, 10, 30, 50, and 100 micrograms/kg on gestation days 10-13) results in dose-related increases in isolated cleft palates and hydronephrotic kidneys in the offspring. TCDF is teratogenic in 100% of the fetuses at dose levels that are not maternally toxic. The fetal kidney is the most sensitive target organ but the kidney lesions may be reversible.

Effects of a polybrominated biphenyl mixture in the rat and mouse. I. Six-month exposure

A 1973 environmental accident in Michigan resulted in exposure of humans via the food chain to polybrominated biphenyl (PBB). To better characterize the toxicity of the halogenated polycyclic aromatic hydrocarbon class of chemicals, rodents were dosed with PBB and their target organs examined for morphological, histological, biochemical, and selected endocrine changes. Male and female rats and mice were given 125 po doses of PBB over a 6-month period at 0.1, 0.3, 1.0, 3.0, and 10.0 mg/kg of body weight/day (5 days/week). There was a dose-related decrease in body weight gain in both male and female rats and male mice. Thymus weights were significantly decreased in all rats exposed to 0.3 mg/kg or more of PBB. Dose-related hepatotoxic effects were observed in both rats and mice characterized by marked increase in liver weight with accentuation of hepatic lobular markings. Microscopically, there were moderate to marked swelling, disorganization, and single cell necrosis of hepatocytes, fatty infiltration, bile duct proliferation, and presence of atypical hyperplastic foci. Hepatic porphyrin levels were markedly increased in both rats and mice primarily in females. There was a significant decrease in serum thyroxine (T4) and triiodothyronine (T3) suggesting that PBB may interfere with thyroid hormone secretion. There was a significant dose-related increase in serum cholesterol and gamma-glutamyl transpeptidase, and a decrease in serum glucose.

Examination of bone marrow, immunologic parameters and host susceptibility following pre- and postnatal exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)

The effects of pre/postnatal exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on various immunological, bone marrow and host susceptibility assays were examined in B6C3F1 hybrid mice. Exposure was accomplished by maternal dosing on Day 14 of gestation and again on Days 1, 7, and 14 following birth, employing dosages of 0, 1.0, 5.0 or 15.0 micrograms/kg body weight. The 15.0 micrograms/kg dosage was lethal to 70% of the offspring with the remainder of that dosage group revealing overt toxicity. Bone marrow toxicity occurred in both the 15.0 and 5.0 micrograms/kg dosage groups as evidenced by bone marrow hypocellularity and depressed colony formation of macrophage-granulocyte progenitor cells and pleuripotent stem cells. Evidence was presented that depression of lymphoproliferative responses following mitogen stimulation in TCDD-immunosuppressed mice was due to a functional defect of lymphocyte activation rather than suppressor cell activity. Administration of either Listeria monocytogenes or syngeneic PYB6 tumor cells in mice exposed to relatively low levels of TCDD during pre- and postnatal development increased their susceptibility to either bacterial or tumor challenge.

Studies on the use of activated charcoal and cholestyramine for reducing the body burden of polybrominated biphenyls

Weanling male rats were exposed to a polybrominated biphenyl (PBB) mixture (Firemaster FF-1) in their diet so that they received 1 mg/kg/day for 6 months. They were then fed a normal diet for 4 months. Following this they were placed on diets containing either activated charcoal (AC) or cholestyramine (CSA) for 6 months to evaluate the usefulness of these compounds in reducing the body burdens of the retained PBBs. Periods of restricted caloric intake were also used in an effort to mobilize PBBs stored in fat. Neither compound nor restricted caloric intake was found to be effective in reducing tissue bromine levels but CSA proved useful in preventing the progression of chronic progressive nephropathy, a spontaneous lesion of aging rats.

Concentration of Egg White by Ultrafiltration 1

Unpasteurized egg white was concentrated by ultrafiltration to about one half of its original volume. Twenty four batches, each started with 5,000 pounds of fresh egg white, were carried out in a 12-month period with a SANOVO Unit in an egg products plant. The optimum operating pressure was found to be about 415 psi. Higher pressure did not benefit the overall efficiency; on the contrary, it increased the chances of fouling and possibly compaction of the membrane and shortened the membrane life. As no refrigeration was provided in the system, egg white temperature rose linearly in all trials. The aerobic plate count of microorganisms was found to be doubled within 1-3 h when the ending temperature was above 20 C and over 10 h when the ending temperature was less than 16 C. The logarithm of permeation rate (R, lb./min) was linearly proportional to operating time (t, min) and the percent solids content of egg white (S). The solids content at a given time can be predicted by the equation: The estimated cost of concentrating egg white from 11.5 to 23% solid and at a volume of 10,000 lb. per day or 2,500,000 lb. per year, was $0.0295 per pound of concentrate. The accountable net savings for liquid egg white which would be shipped in tankers from the west coast to the midwest, and subsequently spray dried, was about $0.0117 per pound of concentrate and $0.0095 for frozen products. The return on capital investment would be approximately 35-40%.