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在饲料中给予斯普拉格-道利大鼠染料木黄酮(CAS编号:446-72-0)的生殖剂量范围查找研究的NTP毒性报告。

NTP toxicity report of reproductive dose range-finding study of Genistein (CAS No. 446-72-0) administered in feed to Sprague-Dawley rats.

作者信息

Delclos K B, Newbold Retha

出版信息

Toxic Rep Ser. 2007 Nov(79):1-C2.

Abstract

Genistein is a naturally occurring isoflavone that interacts with estrogen receptors and multiple other molecular targets. Human exposure to genistein is predominantly through consumption of soy products, including soy-based infant formula and dietary supplements. A series of short-term studies with genistein was conducted with two goals: 1) to obtain data necessary to establish dose levels for subsequent multigeneration reproductive and chronic toxicity studies and 2) to evaluate the effects of genistein on endpoints outside the reproductive tract. The data generated from these studies have been reported previously in the peer-reviewed literature or in technical reports (Appendix C). In addition, selected data from these studies were analyzed and discussed in the National Toxicology Program's Report of the Endocrine Disruptors Low-Dose Peer Review (NTP, 2001). The present report focuses on the reproductive and general toxicology endpoints evaluated. Data obtained in separate evaluations of behavioral, neuroanatomical, neurochemical, and immunological endpoints, as well as the assessment of serum genistein levels, are also discussed to put in better perspective the selection of doses for the multigenerational and chronic studies. Genistein was administered in an irradiated soy- and alfalfa-free diet (Purina 5K96) at exposure concentrations of 0, 5, 25, 100, 250, 625, or 1,250 ppm to 10 vaginal plug-positive, female Sprague-Dawley rats starting on gestation day 7 and continuing throughout pregnancy. These dietary exposure concentrations resulted in ingested doses of approximately 0.3, 1.7, 6.4, 16, 38, and 72 mg genistein/kg body weight to dams in the 5, 25, 100, 250, 625, and 1,250 ppm groups, respectively. Dietary exposure of the dams continued through lactation, during which time ingested doses were approximately 0.6, 3.5, 14, 37, 84, and 167 mg/kg per day. Pups from five litters, culled to eight per litter with an equal sex distribution on postnatal day (PND) 2, were maintained on the same dosed feed as their mothers after weaning until sacrifice at PND 50. Ingested doses were approximately 0.6, 3, 11, 29, 69, and 166 mg/kg per day for male pups and 0.6, 3, 12, 31, 73, and 166 mg/kg per day for female pups. Body weight and feed consumption of the treated dams prior to parturition showed decreasing trends with increasing dose, and both parameters were significantly less than those of the controls in the 1,250 ppm group. A significant exposure concentration-related effect on litter birth weight was observed, but no exposed group differed significantly from the control group in pairwise comparisons. Pups in the 1,250 ppm group had significantly decreased body weights relative to controls at the time of sacrifice (males, 9% decrease; females, 12% decrease). The most pronounced organ weight effects in the pups were decreased ventral prostate weight (absolute weight, 28% decrease; relative weight, 20% decrease) in males at 1,250 ppm and a trend toward higher pituitary gland to body weight ratios in both sexes. Histopathologic examination of female pups revealed ductal/alveolar hyperplasia of the mammary glands at exposure concentrations greater than 250 ppm. Ductal/alveolar hyperplasia and hypertrophy also occurred in males, with significant effects seen at exposure concentrations of 25 ppm or greater for hypertrophy and 250 ppm or greater for hyperplasia. Abnormal cellular maturation (mucocyte metaplasia) in the vagina was observed at 625 and 1,250 ppm, and abnormal ovarian antral follicles were observed at 1,250 ppm. In males, aberrant or delayed spermatogenesis in the seminiferous tubules relative to controls was observed at 1,250 ppm. Histologic evaluation indicated a deficit of sperm in the epididymis at 625 and 1,250 ppm relative to controls, although testicular spermatid head counts and epididymal spermatozoa counts did not show significant differences from controls at these exposure concentrations. Control females showed a high incidence of renal tubule mineralization, and the severity of this lesion was significantly increased at exposure concentrations of 250 ppm or greater. Males showed no renal tubule mineralization below 250 ppm, but incidence and severity increased with increasing exposure concentration at 250 ppm and greater. The primary goal of the current study was to provide information for the selection of exposure concentrations to be used in subsequent multigenerational and chronic studies. These long-term studies were designed to address multiple aspects of the endocrine disruptor hypothesis, that is, the hypothesis that exposures of human and wildlife populations to endocrine-active compounds contribute to adverse reproductive tract effects and cancers of hormone-sensitive organs. In particular, the long-term consequences of low dose exposures that may produce subtle initial effects, the magnification of those effects across generations, and the reversibility of those effects were to be investigated. The goal was to select a high exposure concentration that would not induce overt toxicity in the dams or pups but would induce observable effects in the reproductive organs of the pups without severely impairing fertility in the F1 generation. The 1,250 ppm exposure concentration was clearly ruled out for further testing based on the effects on body weights, histopathologic observations in males and females, and a reduction in the proportion of mated dams producing litters. While the effects observed at 625 ppm would not be predicted to significantly impair reproduction, the observation of significant effects at 250 ppm (hyperplasia in the mammary gland of both sexes), together with the suggestion of subtle effects at this exposure concentration and less in the parallel immunotoxicity and neuroanatomical surveys, a high exposure concentration between 250 and 625 ppm was deemed appropriate for the purposes of the multigenerational reproductive toxicology study and the chronic study of genistein. A high exposure concentration for the multigenerational and chronic studies was thus set at 500 ppm. A low exposure concentration of 5 ppm, where no significant effects were observed in the reproductive dose range-finding, and an intermediate exposure concentration of 100 ppm were also selected. Synonyms: 4',5,7-Trihydroxyisoflavone.

摘要

染料木黄酮是一种天然存在的异黄酮,它可与雌激素受体及多种其他分子靶点相互作用。人类接触染料木黄酮主要是通过食用豆制品,包括大豆基婴儿配方奶粉和膳食补充剂。针对染料木黄酮开展了一系列短期研究,目标有两个:1)获取为后续多代生殖和慢性毒性研究确定剂量水平所需的数据;2)评估染料木黄酮对生殖道以外终点的影响。这些研究产生的数据先前已在同行评审文献或技术报告中报道(附录C)。此外,这些研究中的部分数据在国家毒理学计划的内分泌干扰物低剂量同行评审报告(NTP,2001年)中进行了分析和讨论。本报告重点关注所评估的生殖和一般毒理学终点。还讨论了在行为、神经解剖学、神经化学和免疫学终点的单独评估中获得的数据,以及血清染料木黄酮水平的评估结果,以便更好地理解多代和慢性研究剂量的选择。从妊娠第7天开始,在不含辐照大豆和苜蓿的饮食(普瑞纳5K96)中添加染料木黄酮,以0、5、25、100、250、625或1250 ppm的暴露浓度喂给10只阴道栓阳性的雌性斯普拉格-道利大鼠,并持续整个孕期。这些膳食暴露浓度导致5、25、100、250、625和1250 ppm组的母鼠摄入剂量分别约为0.3、1.7、6.4、16、38和72 mg染料木黄酮/千克体重。母鼠的膳食暴露持续到哺乳期,在此期间摄入剂量约为每天0.6、3.5、14、37、84和167 mg/千克。每窝五只幼崽,在出生后第2天(PND)挑选至每窝八只,雌雄分布均等,断奶后与母亲食用相同的定量饲料,直至在PND 50处死。雄性幼崽的摄入剂量约为每天0.6、3、11、29、69和166 mg/千克,雌性幼崽的摄入剂量约为每天0.6、3、12、31、73和166 mg/千克。分娩前,经处理的母鼠的体重和饲料消耗量随剂量增加呈下降趋势,且1250 ppm组的这两个参数均显著低于对照组。观察到与暴露浓度相关的对窝仔出生体重的显著影响,但在成对比较中,没有暴露组与对照组有显著差异。与对照组相比,1250 ppm组的幼崽在处死时体重显著降低(雄性降低9%;雌性降低12%)。幼崽中最明显的器官重量影响是,1250 ppm组雄性的腹侧前列腺重量降低(绝对重量降低28%;相对重量降低20%),且两性的垂体与体重比有升高趋势。对雌性幼崽的组织病理学检查显示,暴露浓度大于250 ppm时乳腺导管/腺泡增生。雄性也出现导管/腺泡增生和肥大,肥大在暴露浓度25 ppm或更高时出现显著影响,增生在暴露浓度250 ppm或更高时出现显著影响。在625和1250 ppm时观察到阴道细胞异常成熟(粘液细胞化生),在1250 ppm时观察到卵巢窦状卵泡异常。在雄性中,1250 ppm时观察到相对于对照组,生精小管中的精子发生异常或延迟。组织学评估表明,相对于对照组,625和1250 ppm时附睾中的精子数量不足,尽管在这些暴露浓度下,睾丸精子细胞头计数和附睾精子计数与对照组没有显著差异。对照雌性肾小管矿化发生率较高,在暴露浓度250 ppm或更高时,该病变的严重程度显著增加。雄性在250 ppm以下未出现肾小管矿化,但在250 ppm及更高时,发生率和严重程度随暴露浓度增加而增加。本研究的主要目标是为后续多代和慢性研究选择暴露浓度提供信息。这些长期研究旨在解决内分泌干扰物假说的多个方面,即人类和野生动物种群接触内分泌活性化合物会导致生殖道不良影响和激素敏感器官癌症的假说。特别是,要研究可能产生细微初始影响的低剂量暴露的长期后果、这些影响在几代间的放大以及这些影响的可逆性。目标是选择一个高暴露浓度,该浓度不会在母鼠或幼崽中诱发明显毒性,但会在幼崽的生殖器官中诱发可观察到的影响,同时不会严重损害F1代的生育能力。基于对体重的影响、雄性和雌性的组织病理学观察以及产仔的交配母鼠比例降低,1250 ppm的暴露浓度显然被排除用于进一步测试。虽然预计在625 ppm时观察到的影响不会显著损害生殖,但在250 ppm时观察到显著影响(两性乳腺增生),以及在该暴露浓度下存在细微影响的迹象,且在平行的免疫毒性和神经解剖学调查中影响较小,因此认为250至625 ppm之间的高暴露浓度适用于染料木黄酮的多代生殖毒理学研究和慢性研究。因此,多代和慢性研究的高暴露浓度设定为500 ppm。还选择了低暴露浓度5 ppm(在生殖剂量范围查找中未观察到显著影响)和中间暴露浓度100 ppm。同义词:4',5,7-三羟基异黄酮。

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