Carruthers Christina M, Foster Paul M D
National Institute of Environmental Health Sciences, National Institutes of Health, Department of Health and Human Services, Research Triangle Park, North Carolina 27709, USA.
Birth Defects Res B Dev Reprod Toxicol. 2005 Jun;74(3):277-85. doi: 10.1002/bdrb.20050.
Gestational exposure to di-n-butyl phthalate (DBP), a ubiquitous environmental contaminant, has been shown to interfere with the development of the male reproductive tract by acting as an antiandrogen. This study was conducted to identify the critical days for the abnormal development of the male reproductive tract, specifically the testis and epididymis.
Timed-pregnant Sprague-Dawley rats were dosed with DBP at 500 mg/kg/day on gestation day (GD) 14 and 15, 15 and 16, 16 and 17, 17 and 18, 18 and 19, or 19 and 20 (GD 0=plug day). Anogenital distance (AGD) was measured on postnatal day (PND) 1 and 13, while areloa number was recorded on PND 13 only. After weaning, males were allowed to mature to PND 90 at which time they were necropsied. Areloa number and AGD were recorded and testes, epididymides, seminal vesicles, prostate gland, kidneys, and liver weighed. Blood serum was collected and assayed for total testosterone concentration.
There were no observable effects on litter size, sex ratio, serum testosterone concentration, or mortality of pups. Statistically significant permanent reductions in AGD were seen in males exposed prenatally to DBP on GD 15 and 16 or GD 18 and 19. On PND 13, areola were present in males exposed to DBP on GD 15 and 16, 16 and 17, 17 and 18, and 19 and 20. However, permanent retention occurred only in males after DBP exposure on GD 16 and 17. Exposure to DBP on only GD 17 and 18 elicited a reduction in epididymal weights; while exposure on only GD 16 and 17 caused a significant increase in the weights of the testes due to edema. In this study, epididymal and testicular malformations were most prevalent after exposure to DBP on any gestational day. Epididymal malformations, characterized by agenesis of various regions and small or flaccid testes were significantly increased in DBP-exposed males only on GD 16 and 17.
These findings suggest that 2-day DBP exposure is highly detrimental to the developing reproductive tract of the male fetus and the critical window for abnormal development is GD 16-18.
孕期暴露于邻苯二甲酸二正丁酯(DBP)这种普遍存在的环境污染物中,已被证明可作为一种抗雄激素干扰雄性生殖道的发育。本研究旨在确定雄性生殖道,特别是睾丸和附睾异常发育的关键时期。
对定时受孕的斯普拉格-道利大鼠在妊娠第(GD)14和15天、15和16天、16和17天、17和18天、18和19天或19和20天给予500mg/kg/天的DBP(GD 0 = 发现阴栓日)。在出生后第(PND)1天和13天测量肛门生殖器距离(AGD),而仅在PND 13记录乳晕数量。断奶后,雄性大鼠饲养至PND 90,此时进行尸检。记录乳晕数量和AGD,并对睾丸、附睾、精囊、前列腺、肾脏和肝脏称重。采集血清并检测总睾酮浓度。
对窝仔数、性别比例、血清睾酮浓度或幼仔死亡率均未观察到影响。产前在GD 15和16天或GD 18和19天暴露于DBP的雄性大鼠,AGD出现统计学上显著的永久性降低。在PND 13,在GD 15和16天、16和17天、17和18天以及19和20天暴露于DBP的雄性大鼠出现乳晕。然而,仅在GD 16和17天暴露于DBP后的雄性大鼠中出现永久性保留。仅在GD 17和18天暴露于DBP会导致附睾重量减轻;而仅在GD 16和17天暴露会因水肿导致睾丸重量显著增加。在本研究中,在任何妊娠日暴露于DBP后,附睾和睾丸畸形最为普遍。仅在GD 16和17天,暴露于DBP的雄性大鼠中以各区域发育不全以及睾丸小或松软为特征的附睾畸形显著增加。
这些发现表明,2天的DBP暴露对雄性胎儿发育中的生殖道具有高度损害,异常发育的关键窗口期为GD 16 - 18天。