Ryan B M, Selby R, Gingell R, Waechter J M, Butala J H, Dimond S S, Dunn B J, House R, Morrissey R
IIT Research Institute, Chicago, Illinois, USA.
Int J Toxicol. 2001 May-Jun;20(3):121-42. doi: 10.1080/109158101317097700.
This study evaluated the potential reproductive toxicity of phenol in a rat two-generation reproduction study, which included additional study endpoints, such as sperm count and motility, developmental landmarks, histological evaluation of suspect target organs (liver, kidneys, spleen, and thymus), weanling reproductive organ weights, and an immunotoxicity screening plaque assay. Phenol was administered to 30 Sprague-Dawley rats/sex/group in the drinking water at concentrations of 0, 200, 1000, or 5000 ppm. Parental (P1) animals were treated for 10 weeks prior to mating, during mating, gestation, lactation, and until sacrifice. The F1 generation (P1 offspring) was treated using a similar regimen, while the F2 generation was not treated. After mating, 10 P1 males/group were evaluated using standard clinical pathology parameters and an immunotoxicity screening plaque assay. Significant reductions in water and food consumption were observed in the 5000-ppm group in both generations; corollary reductions in body weight/body weight gain were also observed. Mating performance and fertility in both generations were similar to controls, and no adverse effects on vaginal cytology or male reproductive function were observed. Vaginal opening and preputial separation were delayed in the 5000-ppm group, and were considered to be secondary to the reduction in F1 body weight. Litter survival of both generations was reduced in the 5000-ppm group. Absolute uterus and prostate weights were decreased in the F1 generation at all dose levels; however, no underlying pathology was observed and there was no functional deficit in reproductive performance. Therefore, these findings were not considered to be adverse. No evidence of immunotoxicity was noted in the 5000-ppm group. The effects noted at the high concentration were presumed to be associated with flavor aversion to phenol in the drinking water. Based on a comprehensive examination of all parameters, the no-observable-adverse-effect level (NOAEL) for reproductive toxicity of phenol administered in drinking water to rats is 1000 ppm. The corresponding daily intake of phenol for an adult rat at the NOAEL of 1000 ppm is equivalent to about 70 mg/kg/day for males and 93 mg/kg/day for females.
本研究在一项大鼠两代繁殖研究中评估了苯酚的潜在生殖毒性,该研究包括其他研究终点,如精子数量和活力、发育标志、可疑靶器官(肝脏、肾脏、脾脏和胸腺)的组织学评估、断奶时生殖器官重量以及免疫毒性筛选蚀斑试验。将苯酚以0、200、1000或5000 ppm的浓度加入饮用水中,给予每组30只Sprague-Dawley大鼠/性别。亲代(P1)动物在交配前、交配期间、妊娠期、哺乳期直至处死前接受10周的处理。F1代(P1后代)采用类似方案处理,而F2代未接受处理。交配后,每组10只P1雄性大鼠采用标准临床病理学参数和免疫毒性筛选蚀斑试验进行评估。两代中5000 ppm组均观察到水和食物摄入量显著减少;相应地,体重/体重增加也出现减少。两代的交配性能和生育力与对照组相似,未观察到对阴道细胞学或雄性生殖功能的不良影响。5000 ppm组阴道开口和包皮分离延迟,被认为是F1体重降低的继发结果。5000 ppm组两代的窝仔存活率均降低。F1代所有剂量水平下子宫和前列腺绝对重量均降低;然而,未观察到潜在病理学改变,生殖性能也无功能缺陷。因此,这些发现不被认为是有害的。5000 ppm组未发现免疫毒性证据。高浓度时观察到的影响推测与对饮用水中苯酚的味道厌恶有关。基于对所有参数的综合检查,饮用水中给予大鼠的苯酚生殖毒性的无可见不良效应水平(NOAEL)为1000 ppm。在1000 ppm的NOAEL下,成年大鼠苯酚的相应每日摄入量相当于雄性约70 mg/kg/天,雌性约93 mg/kg/天。