PubMed · 247493
The source did not provide an abstract. Follow the original record for more information.
Explore connections, maps & timelines
B Przybojewska. 1978. [Teratogenic action and its effect upon the developing embryo].. https://pubmed.ncbi.nlm.nih.gov/247493/
Cite the original work for its findings. Save a collection to share your selection of sources.
KEEP EXPLORING
Prenatal exposure to the herbicide linuron, a weak androgen receptor antagonist, has been shown to perturb androgen-dependent male rat reproductive development as evidenced by slight decreases in anogenital distance (AGD), increased retention of areolae/nipples, and induction of epididymal malformations in combination with testicular atrophy in the adult rat over dose levels ranging from 12.5 to 100 mg/kg/day. Studies were undertaken to determine whether linuron-mediated changes in AGD and nipple retention are permanent, whether linuron is a direct testicular toxicant, and if there was an association between areola/nipple retention and malformations. Pregnant rats were administered corn oil vehicle or linuron by gavage at 0 or 50 mg/kg/day (n = 8 controls, 20 treated) from gestation days 12 to 21. Male offspring were necropsied on postnatal days (PND) 35 and 56. Linuron-exposed male rats exhibited a significant (8%) decrease in AGD on PND 1 and a similar decrease was also observed on PND 56. Linuron-exposed male rats displayed an increase in areola retention on PND 13, as evidenced by 0.6 +/- 0.5 and 3.3 +/- 0.4 areolae per rat in the control and exposed groups, respectively. Male rats displayed a significant increase in nipple retention on PND 35 and 56 (collectively) of 0 +/- 0.5 and 1.7 +/- 0.3 nipples per rat in control and exposed groups, respectively. On PND 35, 4/51 rats (3/9 litters) from linuron-treated dams displayed enlarged testes in combination with malformed epididymides. Epididymal malformations were observed in 19/51 rats (6/9 litters) in the linuron-exposed dose group. On PND 56, grossly enlarged and edematous testes were seen in 16/56 linuron-exposed rats (6/9 litters). Epididymal lesions were observed in 23/58 rats (6/9 litters). Microscopically, all linuron-exposed animals that exhibited a testicular lesion on PND 56 also displayed an epididymal lesion. These lesions were not seen in control animals. Approximately 25 and 60% of the male offspring that had malformations of the epididymis and vas deferens did not exhibit either areolae on PND 13 or nipples at necropsy, respectively. These data indicate that in utero linuron exposure to 50 mg/kg/day results in permanent changes in AGD and nipple retention in male rats. Moreover, these findings indicate that linuron-induced testicular atrophy, which is observed in adult rats, is secondary to increased intratubular pressure resulting from obstruction of testicular fluid outflow subsequent to malformation of the epididymides. These data also suggest that although linuron-mediated retention of areolae on PND 13 and nipples at necropsy may be suggestive of altered testosterone-mediated reproductive development seen in adult rats, these endpoints are not predictive.
Testosterone plays a major role in male sexual development. Exposure of females to testosterone in utero can induce masculine characteristics such as anovulation, increased anogenital distance (AGD), absence of nipples, retention of male-like tissues, and agenesis of the lower vagina. In addition, high levels of androgens during fetal development can lead to toxic effects such as reduced litter size and viability. The study of the effects of testosterone administration during sexual differentiation provides a foundation for understanding the effects of environmental androgens on fetuses, a sensitive subpopulation. In the current study, we investigated the ability of a range of concentrations of testosterone propionate (TP) administered prenatally to masculinize female and alter male offspring, and measured maternal and fetal T levels. Pregnant Sprague-Dawley rats were dosed by sc injection on gestational day (GD) 14-19 (GD 1= day of plug) with either corn oil (vehicle; 0.1 ml/rat) or with 0.1 ml of TP solution at 0.1, 0.5, 1, 2, 5, or 10 mg/0.1 ml. Parturition was delayed at 2, 5, and 10 mg TP, litter size was reduced at 5 and 10 mg TP, and pup weight was significantly reduced in both sexes at 0.5 mg TP and higher doses. Viability of offspring was unaffected at any dosage level. Androgenic effects seen at 0.5 mg TP in females included increased AGD at weaning and adulthood, reduced number of areolas and nipples, cleft phallus, small vaginal orifice, and presence of prostate tissue. This dose of TP elevated maternal T levels 10x but had no effect on fetal T levels. At 1 mg TP and above, female AGD on postnatal day (PND) 2 (or postcoital day 24 [gestation length = 22(1/2)]) was increased; areolas and nipples were virtually eliminated; levator ani muscle, bulbourethral glands, and seminal vesicles (2 mg TP and above) were present; none of the females developed a vaginal orifice and many females in the 1 and 2 mg TP dose groups developed a greatly distended, fluid-filled uterus after puberty. Maternal T levels at 1 mg TP were elevated 30x, and female fetal T levels showed an 80% increase. Male offspring displayed a reduced AGD and body weight on PND 2 at 0.5 mg TP and higher doses. These effects were not evident by weaning and male offspring displayed no malformations. We conclude that gestational administration of 0.5 and 1 mg TP masculinizes female offspring without greatly affecting pup viability or pregnancy of the dam. This study provides a useful model for in utero testing of environmental androgens for their potential to induce developmental abnormalities.
In female rats, in uteroexposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) during critical periods of organogenesis causes a permanent thread of tissue, consisting of a core of mesenchyme surrounded by keratinized epithelia, across the vaginal opening. The objective of the current study was to determine the earliest time after exposure to TCDD during fetal development that morphological changes in the development of the lower reproductive tract could be detected. In addition, the spatio-temporal expression of several growth factors within the developing reproductive tract was investigated to provide insight into the mechanism of action involved in TCDD-induced vaginal thread formation. Pregnant rats received a single oral dose of 1.0 microg TCDD/kg on gestation day (GD) 15. Dams were sacrificed on GD 17, 18, 19, and 21 and individual reproductive tracts were isolated from female fetuses. As early as GD 18, TCDD produced distinct abnormalities in the female reproductive tract. The width of mesenchyme separating the Mullerian ducts was significantly greater in TCDD-exposed female GD 18 and 19 fetuses and the zone of unfused Mullerian ducts was substantially increased on GD 19 and 21. TCDD induced alterations within the developing reproductive tract in the subcellular and temporal expression of transforming growth factor-beta3 (TGF-beta3) and epidermal growth factor receptor (EGFR). DNA array analysis suggested effects on several genes expressed on GD 18 and 19.