Persistent abnormalities in the rat mammary gland following gestational and lactational exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD).

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) exposure during gestation has revealed reproductive anomalies in rat offspring, including inconclusive reports of stunted mammary development in females (Brown et al., 1998, Carcinogenesis 19, 1623-1629; Lewis et al., 2001, TOXICOL: Sci. 62, 46-53). The current studies were designed to examine mammary-gland development in female offspring exposed in utero and lactationally to TCDD, and to determine a critical exposure period and cellular source of these effects. Long-Evans rats were exposed to 1 microg TCDD/kg body weight (bw) or vehicle on gestation day (GD) 15. TCDD-exposed females sacrificed on postnatal days (PND) 4, 25, 33, 37, 45, and 68 weighed significantly less than control litter mates, and peripubertal animals exhibited delayed vaginal opening and persistent vaginal threads, yet did not display altered estrous cyclicity. Mammary glands taken from TCDD-exposed animals on PND 4 demonstrated reduced primary branches, decreased epithelial elongation, and significantly fewer alveolar buds and lateral branches. This phenomenon persisted through PND 68 when, unlike fully developed glands of controls, TCDD-exposed rats retained undifferentiated terminal structures. Glands of offspring exposed to TCDD or oil on gestation days 15 and 20 or lactation days 1, 3, 5, and 10 were examined on PND 4 or 25 to discern that GD 15 was a critical period for consistent inhibition of epithelial development. Experiments using mammary epithelial transplantation between control and TCDD-exposed females suggested that the stroma plays a major role in the retarded development of the mammary gland following TCDD exposure. Our data suggest that exposure to TCDD prior to migration of the mammary bud into the fat pad permanently alters mammary epithelial development in female rat offspring.     

In utero and lactational 2,3,7,8-tetrachlorodibenzo-p-dioxin exposure: effects on the prostate and its response to castration in senescent C57BL/6J mice.

In utero and lactational 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) exposure inhibits ventral, dorsolateral, and anterior prostate development in C57BL/6 mice. To determine if prostatic abnormalities persist into senescence, mice born to dams given TCDD (5 mug/kg, po) or vehicle on gestation day 13 were examined at 100 and 510 days of age. Half the mice were castrated ten days prior to necropsy in order to assess androgen dependence, while the remaining mice were sham castrated. Effects of TCDD on the dorsolateral and anterior prostate of senescent sham-castrated mice were relatively subtle, whereas the ventral prostate was rudimentary or absent. Castration of vehicle-exposed mice caused far greater reductions in prostate lobe weights, epithelial cell height, and androgen-dependent gene expression (MP25 and probasin) in young mice than in senescent ones, while cell proliferation was decreased by castration in young mice and increased in senescence. Responses to castration were similar at 100 days of age in vehicle- and TCDD-exposed mice. At 510 days, however, TCDD-exposed mice were substantially more responsive to castration by most indices than vehicle-exposed mice. These results demonstrate that prostatic androgen dependence in mice declines substantially with age in several key ways, and that in utero and lactational TCDD exposure protects against this decline. Surprisingly, TCDD increased the incidence of cribriform structures in dorsolateral prostate ducts, from 2-3% in vehicle-exposed senescent mice to 16% in sham-castrated and to 7% in castrated senescent mice. Collectively, these results demonstrate that effects of in utero and lactational TCDD exposure on the prostate persist into senescence, and suggest that in utero and lactational TCDD exposure retards the aging process in the prostate. However, because cribriform structures are often considered to be associated with prostate carcinogenesis, these results also suggest that TCDD exposure early in development may increase susceptibility to prostate cancer.     

In Uteroand Lactational Exposure of the Male Rat to 2,3,7,8-Tetrachlorodibenzo-p-dioxin Impairs Prostate Development: 2. Effects on Growth and Cytodifferentiation

In the male Holtzman rat,in uteroand lactational 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) exposure decreases prostate weight without inhibiting testicular androgen production or decreasing circulating androgen concentrations. Therefore, the present study sought to characterize effects of TCDD exposure on prostate development, from very early outgrowth from the urogenital sinus (Gestation Day [GD] 20) until rapid growth and differentiation are essentially complete (Postnatal Day [PND] 32). Pregnant Holtzman rats were administered a single dose of TCDD (1.0 μg/kg po) or vehicle on GD 15 and offspring were exposed via placental transfer (GD 20 euthanasia) or placental and subsequent lactational transfer until euthanasia (if before PND 21) or weaning. Results show that the prostatic epithelial budding process was impaired byin uteroTCDD exposure, as evidenced by significant decreases in the number of buds emerging from dorsal, lateral, and ventral aspects of the GD 20 urogenital sinus. Ventral prostate cell proliferation index was significantly decreased on PND 1 but was similar to or higher than control at later times, whereas apoptosis was an extremely rare event in ventral prostates from both control and TCDD-exposed animals. Delays were noted in the differentiation of pericordal smooth muscle cells and luminal epithelial cells. In addition, ventral prostates from approximately 40% of TCDD-exposed animals examined on PNDs 21 and 32 exhibited alterations in the histological arrangement of cell types that could not be explained by a developmental delay. Compared to controls, these ventral prostates exhibited a disorganized, hyperplastic epithelium containing fewer luminal epithelial cells and an increased density or continuous layer of basal epithelial cells, as well as thicker periductal smooth muscle sheaths. In addition, in ventral prostates from TCDD-exposed animals, the intensity of androgen receptor staining was relatively low in the central and distal epithelium, and the number of androgen receptor-positive cells was relatively high in the periductal stroma. These data suggest thatin uteroand lactational TCDD exposure interferes with prostate development by decreasing very early epithelial growth, delaying cytodifferentiation, and, in the most severely affected animals, producing alterations in epithelial and stromal cell histological arrangement and the spatial distribution of androgen receptor expression that may be of permanent consequence.     

Radial arm maze performance in rats following gestational and lactational exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)

Recently, we reported that in utero and lactational exposure to 2,3, 7,8-tetrachlorodibenzo-p-dioxin (TCDD) resulted in a task-specific reduction of errors on the radial arm maze (RAM), without similar improvements on other spatial learning tasks including the Morris water maze. The effect was more pronounced in males than in females. This study further investigated the effects of in utero and lactational exposure to TCDD on RAM performance by testing male and female TCDD-exposed rats on either an eight-arm RAM with all arms baited or a 12-arm RAM with 8 of the 12 arms baited. If the rats have improved spatial learning or memory on the RAM, then they should be improved on both RAM tasks; whereas, if they are using adjacent arm selection or some other response strategy to solve the task, they should not show enhanced performance on the 12-arm RAM where not all the arms are rewarded. Time-mated Sprague-Dawley dams were gavaged with corn oil vehicle or one of two doses of TCDD in vehicle (0.1 or 0.2 microg/kg body weight) on gestational days 10 to 16. Litters were culled to eight on day 2 and weaned on day 21. Beginning on day 80, one male and female from each litter was tested on the eight-arm RAM with all arms baited. As in our previous studies, the 0.1-microg/kg TCDD-exposed male rats showed a significant decrease in the number of errors. However, the 0.2-microg/kg males did not differ from the controls. Neither group of TCDD-exposed females differed from the controls. None of the TCDD-exposed rats differed from the controls in adjacent arm selection behavior. An additional male and female from each litter were tested on the 12-arm RAM with only 8 of the 12 arms baited. In this task, neither TCDD group differed from the controls. These results suggest that the reduction of errors on the eight-arm RAM may be due to increased response patterning or use of intramaze cues rather than to improved spatial learning or memory. Also, the reduction in errors was only present at the lower dose of TCDD suggesting that the improvement in performance is only present at very low, nonovertly toxic doses of TCDD.     

Learning and memory in rats gestationally and lactationally exposed to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD).

Recently we reported that in utero and lactational exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) or coplanar polychlorinated biphenyls (PCBs) resulted in a reduction of errors on a radial arm maze (RAM) working memory task. The effect was more pronounced in males than in females. In this study, we further investigated the effects of in utero and lactational exposure to TCDD on learning and memory by testing male and female TCDD-exposed rats on three different spatial learning and memory tasks: the RAM, the Morris water maze (MWM), and spatial discrimination-reversal learning (RL), as well as on a nonspatial learning task, visual RL. Time-mated Sprague-Dawley rats were gavaged with either TCDD (0.1 microg/kg/day) or corn oil vehicle on gestation days 10-16. Litters were culled to eight on day 2 and weaned on day 21. Beginning on day 80, one male and one female from each litter were tested on the same RAM working memory task used in the previous study. Again, the TCDD-exposed male rats displayed a pronounced decrease in errors relative to control males. Following the RAM testing, the same animals were tested on the MWM, but no differences between the exposed and control rats were observed. Another male and female from each litter were tested on spatial RL on a T-maze. There were no differences between the exposed and control rats on this task. Following spatial RL, the same rats were tested on visual RL on the same maze. The exposed animals did not differ from controls on original learning, but took more trials to reach criterion on the first and second reversals. These results demonstrate a reliable, but task-specific, facilitation of spatial learning and memory in male rats exposed to TCDD during gestation and lactation. In contrast, both male and female TCDD-exposed rats showed a deficit in learning on the visual RL task. This pattern is consistent with that seen in earlier monkey studies. Perinatally TCDD-exposed monkeys were facilitated on certain spatial tasks, but impaired on visual RL tasks.     

Estrogenic effect of soy isoflavones on mammary gland morphogenesis and gene expression profile.

We examined the effect of 17beta-estradiol (E2) and soy isoflavones' exposure on morphogenesis and global gene expression in the murine mammary gland. Three exposure regimens were applied: isoflavones added to the diet throughout either the lactational period (via the dams) or the postweaning period and E2 administered orally during the lactational period. Whole mounts of mammary glands were evaluated both in juvenile and adult animals with respect to branching morphogenesis and terminal end bud (TEB) formation. At postnatal day (PND) 28, we observed a significant increase in branching morphogenesis in all treated groups with the most pronounced effect after E2 exposure. For the E2-treated animals there was also a significant increase in TEB formation. At PNDs 42-43 the postweaning isoflavone and the E2 groups showed a transient reduction in the number of TEBs. A similar response after isoflavone and E2 exposure was further substantiated by changes in gene expression, since the same groups of genes were up- and downregulated, particularly in the E2 and postweaning isoflavone regimen. All changes in gene expression correlated with changes in the cellular composition of the gland, i.e., more and larger TEBs and ducts. The results suggest an estrogenic response of physiological doses of isoflavones on mammary gland development at both the morphological and molecular level, which resembled that induced by puberty.     

Mammary gland morphology in Sprague-Dawley rats following treatment with an organochlorine mixture in utero and neonatal genistein.

In a related reproductive toxicology study designed to investigate the effects of in utero exposure to environmental toxicants and potential interaction with postnatal genistein, gross enlargement of thoracic mammary glands was observed in female offspring at 200 days of age. Therefore, the objective of this study was to analyze the effect of in utero exposure to a mixture of toxicants on mammary gland morphology. Time-mated Sprague-Dawley rats were treated on days 9-16 of gestation with vehicle or a mixture of environmental toxicants at 1x the acceptable daily intake. Furthermore, it is unclear whether postnatal exposure to phytoestrogens in soy formulas poses breast cancer benefit or risk, and potential interactions with environmental toxicants are unknown. Therefore, half the female pups from each treatment group received either subcutaneous vehicle or genistein (10 microg/g body weight [bw]/day) on postnatal days 2-8. Following necropsy at 200 days of age, a pathologist, blinded to treatment groups, examined mammary gland histopathology. Only mild histological changes were found in mammary glands of rats exposed to the mixture in utero while pronounced ductal hyperplasia, lactational changes, and fibrosis were observed in mammary glands from the genistein group and were more prominent in the mixture + genistein group. Mammary glands of the control group were histologically normal. Collectively, our results reveal that postnatal exposure to pharmacological levels of genistein induces profound morphological changes in the mammary glands of adult female rats, and that high levels of phytoestrogens possess the potential to modulate the toxicological effects of toxicant mixtures.     

Prenatal 3,3',4,4',5-pentachlorobiphenyl exposure modulates induction of rat hepatic CYP 1A1, 1B1, and AhR by 7,12-dimethylbenz[a]anthracene

Toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) to mouse embryonic teeth, sharing features of early development with salivary glands in common, involves enhanced apoptosis and depends on the expression of epidermal growth factor (EGF) receptor. EGF receptor signaling, on the other hand, is essential for salivary gland branching morphogenesis. To see if TCDD impairs salivary gland morphogenesis and if the impairment is associated with EGF receptor signaling, we cultured mouse (NMRI) E13 submandibular glands with TCDD or TCDD in combination with EGF or fibronectin (FN), both previously found to enhance branching morphogenesis. Explants were examined stereo-microscopically and processed to paraffin sections. TCDD exposure impaired epithelial branching and cleft formation, resulting in enlarged buds. The glands were smaller than normal. EGF and FN alone concentration-dependently stimulated or inhibited branching morphogenesis but when co-administered with TCDD, failed to compensate for its effect. TCDD induced cytochrome P4501A1 expression in the glandular epithelium, indicating activation of the aryl hydrocarbon receptor. TCDD somewhat increased epithelial apoptosis as observed by terminal deoxynucleotidyl transferase (TdT)-mediated nick end-labeling method but the increase could not be correlated with morphological changes. The frequency of proliferating cells was not altered. Corresponding to the reduced cleft sites in TCDD-exposed explants, FN immunoreactivity in the epithelium was reduced. The results show that TCDD, comparably with EGF and FN at morphogenesis-inhibiting concentrations, impaired salivary gland branching morphogenesis in vitro. Together with the failure of EGF and FN at morphogenesis-stimulating concentrations to compensate for the effect of TCDD this implies that TCDD toxicity to developing salivary gland involves reduced EGF receptor signaling.     

In utero exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin causes accelerated terminal differentiation in fetal mouse skin.

2,3,7,8 Tetrachlorodibenzo-p-dioxin (TCDD), a ubiquitous environmental toxin, has been shown to cause a human skin pathology called chloracne. The majority of laboratory mouse strains, with the exception of mice bearing a mutation in thehairless gene, fail to display overt signs of chloracne upon exposure to TCDD. As a result, only minimal data exist on the effects of TCDD in adult haired mice and no data exist on the effects of TCDD in developing mouse skin. Here we report that TCDD affects the temporal expression of protein markers of keratinocyte terminal differentiation during murine skin morphogenesis. Immunohistochemical analysis of E16 mice reveals accelerated expression of the intermediate filament-associated protein filaggrin in response to TCDD. At a later developmental time and after birth, expression of filaggrin and loricrin is indistinguishable between treatment and control groups. At E16 expression of keratins 5, 6, and 10 are unaltered in TCDD-exposed individuals and TUNEL analysis shows no apoptotic cells in the basal and spinous layers of either treatment or control groups. At E16, immunohistochemical analysis of AhR-null mouse skin reveals accelerated filaggrin expression in both vehicle and TCDD exposed animals. We therefore hypothesize that AhR acts as a modulator of late stage keratinocyte terminal differentiation.     

2,3,7,8-tetrachlorodibenzo-p-dioxin inhibits luminal cell differentiation and androgen responsiveness of the ventral prostate without inhibiting prostatic 5alpha-dihydrotestosterone formation or testicular androgen production in rat offspring.

In utero and lactational exposure to a single maternal dose of 1 microg 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD)/kg causes some overt toxicity and impairs prostate growth in male offspring. As similar effects on the ventral prostate can be caused by decreased testosterone production during perinatal development, we determined whether intratesticular testosterone content, testicular responsiveness to gonadotropin stimulation, or plasma testosterone concentrations were reduced in fetal and newborn rats. Because these endpoints were not affected, the ability of TCDD exposure to inhibit synthesis of the proximal androgen in prostate development, 5alpha-dihydrotestosterone (DHT), from the circulating precursor testosterone and 5alpha-androstane-3alpha,17ss-diol (3alpha-Diol), was studied on postnatal days (PNDs) 14, 21, and 32. The ability of the ventral prostate to form DHT from 3alpha-Diol was slightly impaired on PND 14, but this transient effect was not statistically significant, and recovery was evident by PND 21. Subsequent experiments used organ culture to study the effects of in vivo TCDD exposure on androgen metabolism, androgen responsiveness, androgen receptor expression, and luminal epithelial cell differentiation after in vitro exposure to graded androgen concentrations. In utero and lactational TCDD exposure had no effect on DHT formation in organ culture, but transiently reduced the androgen -induced expression of prostatic-binding protein subunit C3, decreased ventral prostate epithelial cell androgen receptor expression, and inhibited the formation of androgen responsive luminal epithelial cells. These results suggest that TCDD exposure impairs prostate growth and androgen responsiveness by inhibiting prostatic epithelial cell differentiation.     

Normal mammary gland morphology in pubertal female mice following in utero and lactational exposure to genistein at levels comparable to human dietary exposure

The objective of the study was to determine the effect of in utero and lactational exposure to genistein (0, 0.1, 0.5, 2.5 and 10 mg/kg/day) on mammary gland morphology in female B6D2F1 mice at levels comparable to or greater than human exposures. The effect of diethylstilbestrol (DES; 0, 0.1, 1, 10 microg/kg/day) on the mammary gland was also examined as a positive estrogenic control. Pregnant females were treated by daily gavage from gestational day 12 to postnatal day (PND) 20. Female offspring were weaned on PND21 and mammary gland whole mounts were examined for growth (length and area of the epithelial tree), proliferation (number of terminal end buds (TEBs)), and differentiation (density of alveolar buds (ABs)) on PND49. The highest dose of DES induced a significant increase in mammary gland growth (P<0.05) and also decreased the number of TEBs (P<0.06). The density of ABs was not significantly affected by DES. By contrast to DES, genistein had no effect on mammary gland morphology at any dose. These results suggest that in utero and lactational exposure to genistein at levels comparable to or greater than human exposures do not adversely affect mammary gland development in pubertal female B6D2F1 mice.     

Altered mammary gland development in male rats exposed to genistein and methoxychlor.

Genistein (GE) is a prevalent phytoestrogen whose presence in human and animal foods may affect biological actions of synthetic endocrine active compounds. We have previously reported that in utero and lactational exposure to high doses of GE or the endocrine active pesticide methoxychlor (MXC) caused mammary epithelial proliferation in 21-day-old male rats. Combined exposure to GE and MXC resulted in significant feminization of the male mammary glands. The goals of the current study were to evaluate mammary responses to GE and MXC at the adult stage and investigate relevant mechanisms. Following in utero, lactational exposure (through maternal diet), and direct dietary exposure, the inguinal mammary gland of male rats (90 days of age) was found to exhibit significant morphological alterations in the groups treated with GE and/or MXC compared to the control. GE exposure (at 300 and 800 ppm concentrations) caused lobular enlargement and epithelial proliferation, whereas MXC exposure (800 ppm) led to ductal elongation and lobular enlargement. Combining the two treatments caused prominent proliferation of both ducts and alveoli; secretory material was seen in readily recognizable alveolar lumens, which are absent in untreated male mammary. We also surveyed gene expression in the mammary tissue using a cDNA microarray and evaluated relevant protein factors. The results indicated that the treatment effects are likely due to interactions between steroid hormone receptor-mediated signals and growth factor-driven cellular pathways. The distinctive responses associated with the GE+MXC combination were likely linked to enhanced actions of insulin-like growth factor 1 and related downstream pathways.     

In utero and lactational exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin in the C57BL/6J mouse prostate: lobe-specific effects on branching morphogenesis.

Branching morphogenesis is an essential component of prostate development. This study was conducted to test the hypothesis that in utero and lactational 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) exposure differentially inhibits branching morphogenesis and ductal canalization in the ventral, dorsal, lateral, and anterior mouse prostate. Pregnant C57BL/6J mice were given TCDD (5 microg/kg, orally) or vehicle on gestation day (GD) 13 and their pups examined at 1, 7, 14, 21, 35, and 90 days of age. Prostate lobes were microdissected after incubation in 0.5% collagenase and the numbers of ductal tips, main ducts, and ductal tips per main duct were determined by examining photographs of microdissected, whole-mount specimens. Ductal canalization was determined using histological sections of the dorsolateral and anterior prostate lobes. TCDD inhibited branching morphogenesis in all prostate lobes. The ventral prostate (VP) was extremely small throughout development and never developed any ductal structure. TCDD reduced the numbers of ductal tips and main ducts in the dorsal (DP) and lateral prostate (LP), but reductions in ductal tip numbers appeared to result entirely from reductions in the number of main ducts. Dorsolateral prostate (DLP) weights were slightly reduced by TCDD, but there was no effect on ductal canalization in the dorsal, lateral, or anterior lobes. TCDD had no effect on main duct number in the anterior prostate, but weight, ductal tip number, and the number of ductal tips per main duct was substantially reduced. These results demonstrate that the severe inhibition in ventral prostate development caused by in utero and lactational TCDD exposure is accompanied by a complete absence of branching morphogenesis. The impairment in dorsal, lateral, and anterior prostate (AP) development is associated with a lobe-specific inhibition of the various processes involved in duct formation.     

Effects of in utero and lactational exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on rat follicular steroidogenesis

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) is a widespread environmental pollutant and causes adverse effects on female reproduction when administered to rats. Our aims were to study effects of gestational and lactational exposure to TCDD on ovarian steroidogenesis and steroidogenic enzyme expression of offspring on postnatal day (PND) 14 in the rat and sensitivity of enzymatically isolated ovarian follicles to TCDD in vitro. Synthetic estrogen diethylstilbestrol (DES) was used as a treatment control. Serum progesterone (P4) level in offspring increased significantly on PND 14 in the TCDD (1 microg/kg)-exposed group while body weight, FSH and E2 levels were not changed. In ovarian follicles of offspring on PND 14 in the TCDD-exposed groups, protein expression of cytochrome P-450 aromatase, cytochrome P-450 cholesterol side-chain cleavage, steroidogenic acute regulatory protein, 3beta-hydroxy-steroid-dehydrogenase/Delta(5)-Delta(4) isomerase type 1, or P4 receptor was not affected. TCDD decreased E2 and P4 production in ex vivo follicle culture. DES at a dose level of 0.1mg/kg was dystocic while a dose 0.02 mg/kg increased ovarian ex vivo E2 and testosterone production without affecting P450arom activity indicating stimulation of early steps of steroidogenic pathway. Data suggests that TCDD has multiple targets in ovarian steroidogenesis, but the inhibitory action represented as decreased follicular steroid hormone production ex vivo is not apparent at the ovarian protein expression. Furthermore, TCDD had no direct effect on immature rat ovarian steroidogenesis in vitro suggesting that the follicle culture method is not a sensitive method to study the mechanisms of TCDD action.     

Abnormal peripubertal development of the rat mammary gland following exposure in utero and during lactation to a mixture of genistein and the food contaminant vinclozolin

The impact of early exposure to endocrine disruptor mixtures on mammary gland development is poorly known. Here, we identify the effects of a conception to weaning exposure of rats to the phytoestrogen genistein (G) and/or the antiandrogen vinclozolin (V) at 1 mg/kg-d, alone or in association. Using several approaches, we found that G- and GV-exposed rats displayed significantly greater epithelial branching and proliferation, wider terminal end buds than controls at PND35, as well as ductal hyperplasia and periductal fibrosis. Focal branching defects were present in V-exposed rats. An increased ER and AR expression was observed in G- and GV- as compared to V-exposed rats at PND35. Surprisingly, a significant number of GV- and to a lesser extent, V-exposed animals displayed abnormal hyperplasic alveolar structures at PND50. Thus, gestational and lactational exposure to low doses of genistein plus vinclozolin may seriously affect peripubertal development of the rat mammary gland.     

Critical role of microsomal prostaglandin E synthase-1 in the hydronephrosis caused by lactational exposure to dioxin in mice

Hydronephrosis induced in the kidney of neonatal mice exposed to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) via lactation is a sensitive and characteristic hallmark of TCDD teratogenicity. We previously found that cyclooxygenase-2 (COX-2) activity induced in mouse neonate kidneys by lactational TCDD exposure is required for this toxicity. COX-2 is an inducible form of cyclooxygenase and is responsible for producing prostaglandins (PGs) and thromboxane. PGE(2), a prostaglandin, is elevated in TCDD-exposed mouse pups. In this study, we investigated the role of microsomal prostaglandin E synthase-1 (mPGES-1), an inducible form of PGE(2) synthase, in TCDD-induced hydronephrosis. A dose of 10 μg TCDD/kg to dams increased mPGES-1 messenger RNA abundance, urinary PGE(2) levels, and the incidence of hydronephrosis in mPGES-1 wild-type pups. In homozygous mPGES-1 knockout (KO) mice, in contrast, TCDD-induced hydronephrosis was suppressed, demonstrating an essential role of mPGES-1 in the response. Lack of the mPGES-1 gene also suppressed urinary PGE(2) level to near the basal level in TCDD-exposed pups. In conclusion, mPGES-1 upregulation upon lactational TCDD exposure is a causal factor for TCDD-induced hydronephrosis in mouse neonates.     

Repeated in utero and lactational 2,3,7,8-tetrachlorodibenzo-p-dioxin exposure affects male gonads in offspring, leading to sex ratio changes in F2 progeny

The effects of in utero and lactational 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) on the reproductive system of male rat offspring (F1) and the sex ratio of the subsequent generation (F2) were examined. Female Holtzman rats were gavaged with an initial loading dose of 400 ng/kg TCDD prior to mating, followed by weekly maintenance doses of 80 ng/kg during mating, pregnancy, and the lactation period. Maternal exposure to TCDD had no significant effects on fetus/pup (F1) mortality, litter size, or sex ratio on gestation day (GD) 20 or postnatal day (PND) 2. The TCDD concentration in maternal livers and adipose tissue on GD20 was 1.21 and 1.81 ng/kg, respectively, and decreased at weaning to 0.72 in the liver and 0.84 in the adipose tissue. In contrast, the TCDD concentration in pup livers was 1.32 ng/kg on PND2 and increased to 1.80 ng/kg at weaning. Ventral prostate weight of male offspring was significantly decreased by TCDD exposure on PND28 and 120 compared with that of controls. Weight of the testes, cauda epididymides, and seminal vesicle, and sperm number in the cauda epididymis were not changed by TCDD exposure at PND120. TCDD- or vehicle-exposed male offspring were mated with unexposed females. The sex ratio (percentage of male pups) of F2 offspring was significantly reduced in the TCDD-exposed group compared with controls. These results suggest that in utero and lactational TCDD exposures affect the development of male gonads in offspring (F1), leading to changes in the sex ratio of the subsequent generation (F2).     

In utero and lactational exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin alters postnatal development of seminal vesicle epithelium.

2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD) has been shown to alter male reproductive development of laboratory animals through in utero and lactational exposure. As a result of exposure, the accessory glands of the male reproductive tract, including the seminal vesicle, are decreased in size as determined by total weight of the tissue. Analysis of seminal vesicle weights over time suggests that the changes may be transient. Administration of 1.0 microg/kg TCDD during gestation caused a significant decrease in seminal vesicle weights of offspring 8-11 months of age. We examined the effects of TCDD on seminal vesicles from rats exposed in utero and lactationally. Pregnant Long Evans rats were gavaged on gestation day 15 with 1.0 microg/kg TCDD in corn oil. Male pups were euthanized and necropsied on postnatal days (PND) 15, 25, 32, 49, 63, and 120. Seminal vesicles were weighed and then fixed in 10% neutral buffered formalin and processed for microscopic examination. Seminal vesicle weights were not significantly decreased until PND 32. Androgen receptor mRNA expression in PND 25 seminal vesicles was not different from control. In the present study, TCDD exposure decreased seminal vesicle epithelial branching and differentiation. Control epithelial cells had tall columnar morphology with relatively abundant cytoplasm, whereas TCDD-treated cells had rounded nuclei and less cytoplasm. In addition, immunolocalization of proliferating nuclear antigen was confined to undifferentiated basal epithelial cells of controls but was found in both basal and luminal cells of the treated seminal vesicle. Results indicate that the TCDD-induced impaired growth of the rat seminal vesicles is associated with a dramatic decrease in the development of the epithelium.     

Altered mammary gland differentiation and progesterone receptor expression in rats fed soy and whey proteins.

There are suspected links between an animal's diet, differentiation status of a target tissue, and sensitivity to chemically induced cancer. We have demonstrated that rats fed AIN93G diets made with soy protein isolate (SPI) or whey protein hydrolysate (WPH) had a lower incidence of 7,12-dimethylbenz(a)anthracene (DMBA)-induced adenocarcinoma than rats fed the same diet made with casein (CAS). The current study was conducted to determine the differentiation status of the mammary glands during development. Offspring of rats (n = 5-10/group) were fed diets made with SPI, WPH, or CAS throughout life (beginning on gestation day 4) and were sacrificed on postnatal day (PND) 21, PND 33, PND 50 or on metaestrous between PND 48 and PND 51. There were no significant differences between the numbers of mammary terminal end buds (TEBs) or lobuloalveoli (LOB) between any of the diets groups at PND 21 or PND 33, but at PND 50 there was an 75% decrease in the mean numbers of TEBs/mm(2) in the SPI- or WPH-fed rats, compared with the CAS-fed rats (p = 0.09 and p = 0.06, respectively). In rats sacrificed in metaestrous, there were no significant differences in the proliferation index (PI) in the TEBs or LOB between any of the diet groups. In metaestrous rats, there were twice as many cells expressing estrogen receptor beta (ERbeta; approximately 60%) compared with estrogen receptor alpha (ERalpha; approximately 30%) in the LOB and 1.5 times more ERbeta (approximately 60%) compared with estrogen receptor alpha (ERalpha, approximately 40%) in the TEBs. There were no diet-dependent differences in expression of ERalpha and ERbeta. Similarly, there were no differences between the diet groups in progesterone receptor (PR) expressing LOB cells. However, in the TEBs there was a diet-dependent difference in PR positive cells with a 34% increase (p < 0.05) in the SPI-fed rats and a 38% increase (p < 0.05) in the WPH-fed rats compared with the CAS-fed rats. These results show that the type of dietary protein alters the phenotype of mammary epithelia in the TEBs. The SPI- and WPH-dependent changes in mammary differentiation may contribute to the reduced sensitivity to DMBA-induced mammary cancer in rats fed these proteins.