Tyl Rochelle W, Myers Christina B, Marr Melissa C, Sloan Carol S, Castillo Nora P, Veselica M Michael, Seely John C, Dimond Stephen S, Van Miller John P, Shiotsuka Ronald N, Beyer Dieter, Hentges Steven G, Waechter John M
Health Sciences Unit, RTI International, Research Triangle Park, North Carolina 27709, USA.
Toxicol Sci. 2008 Aug;104(2):362-84. doi: 10.1093/toxsci/kfn084. Epub 2008 Apr 29.
Dietary bisphenol A (BPA) was evaluated in a mouse two-generation study at 0, 0.018, 0.18, 1.8, 30, 300, or 3500 ppm (0, 0.003, 0.03, 0.3, 5, 50, or 600 mg BPA/kg/day, 28 per sex per group). A concurrent positive control group of dietary 17beta-estradiol (0.5 ppm; 28 per sex) confirmed the sensitivity of CD-1 mice to an endogenous estrogen. There were no BPA-related effects on adult mating, fertility or gestational indices, ovarian primordial follicle counts, estrous cyclicity, precoital interval, offspring sex ratios or postnatal survival, sperm parameters or reproductive organ weights or histopathology (including the testes and prostate). Adult systemic effects: at 300 ppm, only centrilobular hepatocyte hypertrophy; at 3500 ppm, reduced body weight, increased kidney and liver weights, centrilobular hepatocyte hypertrophy, and renal nephropathy in males. At 3500 ppm, BPA also reduced F1/F2 weanling body weight, reduced weanling spleen and testes weights (with seminiferous tubule hypoplasia), slightly delayed preputial separation (PPS), and apparently increased the incidence of treatment-related, undescended testes only in weanlings, which did not result in adverse effects on adult reproductive structures or functions; this last finding is considered a developmental delay in the normal process of testes descent. It is likely that these transient effects were secondary to (and caused by) systemic toxicity. Gestational length was increased by 0.3 days in F1/F2 generations; the toxicological significance, if any, of this marginal difference is unknown. At lower doses (0.018-30 ppm), there were no treatment-related effects and no evidence of nonmonotonic dose-response curves for any parameter. The systemic no observable effect level (NOEL) was 30 ppm BPA (approximately 5 mg/kg/day); the reproductive/developmental NOEL was 300 ppm (approximately 50 mg/kg/day). Therefore, BPA is not considered a selective reproductive or developmental toxicant in mice.
在一项小鼠两代研究中,对膳食中的双酚A(BPA)进行了评估,剂量分别为0、0.018、0.18、1.8、30、300或3500 ppm(相当于0、0.003、0.03、0.3、5、50或600毫克双酚A/千克/天,每组每种性别28只)。同时设置了一个膳食中添加17β-雌二醇(0.5 ppm;每种性别28只)的阳性对照组,以证实CD-1小鼠对内源性雌激素的敏感性。双酚A对成年小鼠的交配、生育力或妊娠指数、卵巢原始卵泡计数、发情周期、交配前间隔、后代性别比例或出生后存活率、精子参数或生殖器官重量及组织病理学(包括睾丸和前列腺)均无相关影响。成年小鼠的全身效应:在300 ppm时,仅出现中央小叶肝细胞肥大;在3500 ppm时,雄性小鼠体重减轻、肾脏和肝脏重量增加、中央小叶肝细胞肥大以及出现肾病。在3500 ppm时,双酚A还降低了F1/F2代断奶幼鼠的体重,减轻了断奶幼鼠脾脏和睾丸的重量(伴有生精小管发育不全),轻微延迟了包皮分离(PPS),并且仅在断奶幼鼠中明显增加了与治疗相关的隐睾发生率,但这并未对成年生殖结构或功能产生不良影响;最后这一发现被认为是睾丸下降正常过程中的发育延迟。这些短暂效应可能是全身毒性的继发效应(并由其引起)。F1/F2代的妊娠期延长了0.3天;这种微小差异的毒理学意义(如果有)尚不清楚。在较低剂量(0.018 - 30 ppm)下,未观察到与治疗相关的效应,也没有任何参数出现非单调剂量反应曲线的证据。全身未观察到有害作用水平(NOEL)为30 ppm双酚A(约5毫克/千克/天);生殖/发育NOEL为300 ppm(约50毫克/千克/天)。因此,双酚A在小鼠中不被视为选择性生殖或发育毒物。