Hurst C H, Abbott B D, DeVito M J, Birnbaum L S
University of North Carolina, Chapel Hill 27599-7270, USA.
Toxicol Sci. 1998 Oct;45(2):129-36. doi: 10.1006/toxs.1998.2520.
Prenatal exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) interferes with fetal development at doses lower than those causing overt toxicity in adult animals. In a multigeneration study (Murray et al., 1979), female rats that were administered 0.01 microgram TCDD/kg/day in their diet did not experience reduced fertility; however, reduced fertility was seen in the F1 and F2 generations. Exposure to TCDD during development produces alterations in the reproductive system of the developing pups, such as delayed puberty and reduced sperm counts in males (Mably et al., 1992a; Gray et al., 1995) and malformations in the external genitalia of females (Gray and Ostby, 1995). Therefore, the objectives of this study were to determine maternal and fetal tissue concentrations of TCDD that are associated with the adverse reproductive effects seen by Gray and co-workers. Pregnant Long Evans rats received a single oral dose of 1.15 micrograms [3H]TCDD/kg on Gestation Day (GD) 8 and maternal as well as fetal tissue concentrations of TCDD were measured on GD9, GD16, and GD21. On GD9, the highest level of TCDD localized in the maternal liver (25.1% dose). In addition, the amount reaching all the embryos on GD9 was 0.01% of the administered dose, which resulted in a concentration of 0.02% dose/g. The amount of TCDD reaching the fetal compartment (fetuses + placentas) increased to 0.12% dose/tissue on GD16 and 0.71% by GD21. The concentration of TCDD within the fetal compartment (0.01% dose/g) on GD16 was comparable to that found in the maternal blood and spleen. Concentrations of TCDD in a single embryo/fetus were 39.6, 18.1, and 22.1 pg/g on GD9, GD16, and GD21, respectively. Estimates of hepatic half-life of elimination in pregnant rats suggested that TCDD may be eliminated faster in pregnant LE rats. Therefore, measurements of biliary elimination were made in pregnant and nonpregnant LE rats to compare rates of metabolism; however, biliary elimination of TCDD is not affected by pregnancy. In conclusion, this dose administered during a critical period of organogenesis causes adverse effects on the developing reproductive system of rodents. This dose produced a body burden of 22.1 pg TCDD/g within a single fetus on GD21. This indicates that low-level TCDD exposure during the perinatal stage of life can produce adverse effects within the developing pups.
产前接触2,3,7,8 - 四氯二苯并 - 对 - 二噁英(TCDD)会在低于导致成年动物明显毒性的剂量下干扰胎儿发育。在一项多代研究中(Murray等人,1979年),在饮食中给予0.01微克TCDD/千克/天的雌性大鼠生育能力并未降低;然而,在F1和F2代中观察到生育能力下降。发育期间接触TCDD会使发育中的幼崽生殖系统发生改变,如雄性青春期延迟和精子数量减少(Mably等人,1992a;Gray等人,1995年)以及雌性外生殖器畸形(Gray和Ostby,1995年)。因此,本研究的目的是确定与Gray及其同事所观察到的不良生殖效应相关的母体和胎儿组织中TCDD的浓度。怀孕的Long Evans大鼠在妊娠第8天接受单次口服剂量为1.15微克[3H]TCDD/千克,并在妊娠第9天、第16天和第21天测量母体和胎儿组织中TCDD的浓度。在妊娠第9天,TCDD的最高水平定位于母体肝脏(剂量的25.1%)。此外,在妊娠第9天到达所有胚胎的TCDD量为给药剂量的0.01%,这导致浓度为0.02%剂量/克。到达胎儿区室(胎儿 + 胎盘)的TCDD量在妊娠第16天增加到0.12%剂量/组织,到妊娠第21天增加到0.71%。妊娠第16天胎儿区室内TCDD的浓度(0.01%剂量/克)与母体血液和脾脏中的浓度相当。在妊娠第9天、第16天和第21天单个胚胎/胎儿中TCDD的浓度分别为39.6、18.1和22.1皮克/克。对怀孕大鼠肝脏消除半衰期的估计表明,TCDD在怀孕的LE大鼠中可能消除得更快。因此,对怀孕和未怀孕的LE大鼠进行了胆汁消除测量以比较代谢率;然而,TCDD的胆汁消除不受怀孕影响。总之,在器官发生的关键时期给予的该剂量对啮齿动物发育中的生殖系统产生了不良影响。该剂量在妊娠第21天导致单个胎儿体内TCDD的身体负担为22.1皮克/克。这表明围产期低水平接触TCDD会在发育中的幼崽体内产生不良影响。