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

Toxicity report series Pub Date : 2007-11-01
K B Delclos, Retha Newbold
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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.</p>","PeriodicalId":23116,"journal":{"name":"Toxicity report series","volume":" 79","pages":"1-C2"},"PeriodicalIF":0.0000,"publicationDate":"2007-11-01","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Toxicity report series","FirstCategoryId":"1085","ListUrlMain":"","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
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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.

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染料木黄酮(CAS No. 446-72-0)在Sprague-Dawley大鼠饲料中的生殖剂量范围研究的NTP毒性报告。
染料木素是一种天然存在的异黄酮,与雌激素受体和多种其他分子靶点相互作用。人类接触染料木素主要是通过食用豆制品,包括以大豆为基础的婴儿配方奶粉和膳食补充剂。本研究对染料木素进行了一系列短期研究,目的有两个:1)为后续多代生殖和慢性毒性研究获取必要的数据,以建立剂量水平;2)评估染料木素对生殖道外终点的影响。这些研究产生的数据以前已在同行评议文献或技术报告中报告过(附录C)。此外,国家毒理学计划的《内分泌干扰物低剂量同行评议报告》(NTP, 2001年)对这些研究中选定的数据进行了分析和讨论。本报告的重点是评估的生殖和一般毒理学终点。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,以及血清染料木素水平的评估,也被讨论,以便更好地了解多代和慢性研究的剂量选择。从妊娠第7天开始,将染料木素添加到不含大豆和苜蓿的辐照饲料(Purina 5K96)中,暴露浓度分别为0、5、25、100、250、625或1250 ppm,给10只阴道插入阳性的雌性Sprague-Dawley大鼠,并持续整个妊娠期。这些饮食暴露浓度分别导致5,25,100,250,625和1,250 ppm组的水坝摄入约0.3,1.7,6.4,16,38和72 mg染料木素/kg体重。哺乳期间,哺乳母鼠的饮食暴露量分别为每天0.6、3.5、14、37、84和167 mg/kg。在出生后第2天(PND),从5窝幼崽中挑选出8窝幼崽,在断奶后与它们的母亲保持相同的饲料剂量,直到PND 50献祭。雄性幼崽每天摄入的剂量分别为0.6、3、11、29、69和166 mg/kg,雌性幼崽每天摄入的剂量分别为0.6、3、12、31、73和166 mg/kg。1250 ppm组产仔前体重和采食量随剂量的增加呈下降趋势,且均显著低于对照组。在两两比较中,暴露组与对照组没有显著差异,但暴露浓度对雏鸟出生体重有显著影响。1250 ppm组的幼崽在献祭时体重相对于对照组显著下降(雄性,下降9%;雌性减少12%)。幼犬最显著的器官重量效应是腹侧前列腺重量减少(绝对重量,减少28%;在1,250 PPM时,男性的相对体重下降20%),两性垂体与体重之比都有升高的趋势。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/肺泡增生。导管/肺泡增生和肥大也发生在男性身上,在暴露浓度为25ppm或更高的情况下,肥大和增生的影响显著,暴露浓度为250ppm或更高。在625和1250 ppm下观察到阴道内异常的细胞成熟(粘膜细胞化生),在1250 ppm下观察到卵巢窦卵泡异常。在男性中,相对于对照组,在1,250 ppm时观察到精管中精子发生异常或延迟。组织学评估表明,在625 ppm和1250 ppm浓度下,与对照组相比,附睾中的精子数量减少,尽管睾丸精细胞头数和附睾精子数量在这些暴露浓度下与对照组没有显着差异。对照女性表现出高发生率的肾小管矿化,这种损害的严重程度在暴露浓度为250 ppm或更高时显着增加。在250 ppm以下,男性肾小管矿化不明显,但随着暴露浓度的增加,发病率和严重程度增加。本研究的主要目的是为选择暴露浓度提供信息,以便在随后的多代和慢性研究中使用。这些长期研究旨在解决内分泌干扰物假说的多个方面,即人类和野生动物群体暴露于内分泌活性化合物会导致不利的生殖道影响和激素敏感器官癌症的假说。 特别是,将研究可能产生细微初始影响的低剂量照射的长期后果、这些影响在几代人之间的放大程度以及这些影响的可逆性。目的是选择一个高暴露浓度,既不会对母鼠或幼崽产生明显的毒性,又会对幼崽的生殖器官产生可观察到的影响,同时又不会严重损害F1代的生育能力。根据对体重的影响、对雄性和雌性的组织病理学观察以及交配产卵的比例的减少,1250 ppm的暴露浓度显然被排除在进一步的测试之外。虽然625百万分之一的浓度所观察到的影响预计不会显著损害生殖,但250百万分之一的浓度所观察到的显著影响(两性乳腺增生),以及在此暴露浓度下的微妙影响,而在平行的免疫毒性和神经解剖学调查中,影响较小,对于多代生殖毒理学研究和染料木素慢性研究而言,250至625 PPM之间的高暴露浓度被认为是合适的。因此,多代和慢性研究的高暴露浓度设定为500ppm。还选择了5百万分之一的低暴露浓度,在此浓度下对生殖剂量范围测定没有观察到重大影响,并选择了100百万分之一的中等暴露浓度。同义词:4 ',5,7-Trihydroxyisoflavone。
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