Toxicology and carcinogenesis studies of genistein (Cas No. 446-72-0) in Sprague-Dawley rats (feed study).

Q4 Medicine National Toxicology Program technical report series Pub Date : 2008-01-01
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Because of these concerns, genistein was selected as one of the compounds to be examined using a protocol designed to evaluate the effects of multigenerational and long-term exposures to doses of estrogenic agents that produce subtle reproductive tract lesions in developmentally exposed Sprague-Dawley rat pups. Results from the 2-year study are reported here, and results from the multigenerational reproductive toxicology feed study are reported separately (NTP, 2008a). Data from a preliminary dose range-finding feed study (NTP, 2007) that utilized exposure concentrations up to 1,250 ppm genistein were used to select dietary exposure concentrations of 0, 5, 100, and 500 ppm for the current study. The multigenerational reproductive toxicology study examined F(0) through F(4) generations with F(5) litters terminated at weaning and focused on reproductive endpoints (NTP, 2008a). Animals were exposed from the time that the F(0) generation was 6 weeks old through weaning of the F(3) generation, and animals of the F(0) through F(4) generations were necropsied at 20 weeks of age. The current study was a 2-year dietary study utilizing three exposure arms: continuous exposure from conception through 2 years (designated F(1) continuous, or F(1)C), exposure from conception through 20 weeks followed by control diet to 2 years [designated F(1) truncated at postnatal day (PND) 140, or F(1)T140], and exposure from conception through weaning followed by control diet to 2 years (designated F(3) truncated at PND 21, or F(3)T21). The \"F(3)\" designation for the F(3)T21 arm indicates that these animals were siblings of the F(3) animals from the multigenerational reproductive toxicology study (NTP, 2008a). The F(1)C and F(1)T140 animals were also siblings but were derived from a separate breeding that was identical to the procedure used to produce the F(1) generation of the multigenerational reproductive toxicology study. The animals in this study were exposed to genistein during various phases of their lives from conception until termination at 2 years, and the ingested doses varied over the course of the study. During pregnancy, the ingested doses of the dams were approximately 0, 0.5, 9, or 45 mg/kg body weight per day. During lactation, the dams' ingested doses were 0, 0.7, 15, or 75 mg/kg per day. Supplementary studies, which are described in the multigenerational reproductive toxicology study, indicated minimal transfer of genistein to pups via the dams' milk. The mean directly ingested genistein doses during the period prior to PND 140 were approximately 0.4, 8, or 44 mg/kg per day for females and 0.4, 7, or 37 mg/kg per day for males. For the period between PND 140 and the end of the study, mean ingested doses were approximately 0.3, 5, or 29 mg/kg per day for females and 0.2, 4, or 20 mg/kg per day for males. For the current study, 50 animals per sex were initially assigned to each exposure group in each arm of the study. In control groups, histopathology data from one to four additional animals that had been assigned as sentinels but that became moribund or died early were also included in the analysis and presentation. Survival was similar in all control and exposed groups and ranged from 62% to 86% for males and 43% to 64% for females. Mean body weights of 500 ppm F(1)C females were less than those of the controls throughout the study. Mean body weights of 500 ppm F(1)T140 rats were less than those of the controls throughout the study. In females of all study arms (F(1)C, F(1)T140, and F(3)T21) an early onset of aberrant estrous cycles, suggesting early reproductive senescence, was observed in the 500 ppm groups. In the F(3)T21 arm, there were also significant effects on the onset of aberrant estrous cycles in the 5 and 100 ppm groups. Pituitary gland weights were significantly increased in females in the 500 ppm groups of the F(1)C and F(1)T140 study arms and in the 100 ppm group of the F(3)T21 arm. In F(1)C females, there was a significant positive trend in the incidences of mammary gland adenoma or adenocarcinoma (combined) regardless of whether an unmodified or natural log-transformed dose scale was used in the analysis, and the incidence in the 500 ppm group was significantly greater than that in the control group. A significant negative trend occurred in the incidences of benign mammary gland fibroadenoma in F(1)C females, and the incidence in the 500 ppm group was significantly less than that in the control group. In 5 and 100 ppm F(1)T140 females, the combined incidences of adenoma and adenocarcinoma were less than those in the control or 500 ppm groups, although these were not statistically significant differences. When the natural log-transformed dose scale was used, a marginally significant positive trend occurred in the incidences of adenoma or adenocarcinoma (combined) in F(3)T21 females. There were positive trends in the incidences of adenoma or carcinoma (combined) in the pars distalis of the pituitary gland of females in the F(1)C and F(1)T140 arms, and the incidence in the 500 ppm group was significantly greater than that in the controls in the F(1)C study arm. In F(1)C males, a significant positive trend (unmodified dose scale only) occurred in the incidences of combined adenoma or carcinoma of the pancreatic islets. While the incidence in the 500 ppm group was elevated relative to that in the control group (6/49 versus 1/49), this was not statistically significant. The fact that transitional lesions (i.e., hyperplasia) were not observed combined with variable control rates in males of this substrain of rats led to the conclusion that this lesion was not likely to be related to genistein treatment.</p><p><strong>Conclusions: </strong>Under the conditions of this 2-year feed study with continuous exposure to the test compound from conception through termination (F(1)C), there was no evidence of carcinogenic activity of genistein in male Sprague-Dawley rats exposed to 5, 100, or 500 ppm. 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引用次数: 0

Abstract

Unlabelled: 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. Consumption of soy and genistein has been associated with a variety of beneficial effects in animals and humans, but concerns have also been raised regarding potential adverse effects of genistein, particularly with regard to reproductive toxicity and the induction or potentiation of carcinogenesis, due primarily to its weak estrogenic activity. Because of these concerns, genistein was selected as one of the compounds to be examined using a protocol designed to evaluate the effects of multigenerational and long-term exposures to doses of estrogenic agents that produce subtle reproductive tract lesions in developmentally exposed Sprague-Dawley rat pups. Results from the 2-year study are reported here, and results from the multigenerational reproductive toxicology feed study are reported separately (NTP, 2008a). Data from a preliminary dose range-finding feed study (NTP, 2007) that utilized exposure concentrations up to 1,250 ppm genistein were used to select dietary exposure concentrations of 0, 5, 100, and 500 ppm for the current study. The multigenerational reproductive toxicology study examined F(0) through F(4) generations with F(5) litters terminated at weaning and focused on reproductive endpoints (NTP, 2008a). Animals were exposed from the time that the F(0) generation was 6 weeks old through weaning of the F(3) generation, and animals of the F(0) through F(4) generations were necropsied at 20 weeks of age. The current study was a 2-year dietary study utilizing three exposure arms: continuous exposure from conception through 2 years (designated F(1) continuous, or F(1)C), exposure from conception through 20 weeks followed by control diet to 2 years [designated F(1) truncated at postnatal day (PND) 140, or F(1)T140], and exposure from conception through weaning followed by control diet to 2 years (designated F(3) truncated at PND 21, or F(3)T21). The "F(3)" designation for the F(3)T21 arm indicates that these animals were siblings of the F(3) animals from the multigenerational reproductive toxicology study (NTP, 2008a). The F(1)C and F(1)T140 animals were also siblings but were derived from a separate breeding that was identical to the procedure used to produce the F(1) generation of the multigenerational reproductive toxicology study. The animals in this study were exposed to genistein during various phases of their lives from conception until termination at 2 years, and the ingested doses varied over the course of the study. During pregnancy, the ingested doses of the dams were approximately 0, 0.5, 9, or 45 mg/kg body weight per day. During lactation, the dams' ingested doses were 0, 0.7, 15, or 75 mg/kg per day. Supplementary studies, which are described in the multigenerational reproductive toxicology study, indicated minimal transfer of genistein to pups via the dams' milk. The mean directly ingested genistein doses during the period prior to PND 140 were approximately 0.4, 8, or 44 mg/kg per day for females and 0.4, 7, or 37 mg/kg per day for males. For the period between PND 140 and the end of the study, mean ingested doses were approximately 0.3, 5, or 29 mg/kg per day for females and 0.2, 4, or 20 mg/kg per day for males. For the current study, 50 animals per sex were initially assigned to each exposure group in each arm of the study. In control groups, histopathology data from one to four additional animals that had been assigned as sentinels but that became moribund or died early were also included in the analysis and presentation. Survival was similar in all control and exposed groups and ranged from 62% to 86% for males and 43% to 64% for females. Mean body weights of 500 ppm F(1)C females were less than those of the controls throughout the study. Mean body weights of 500 ppm F(1)T140 rats were less than those of the controls throughout the study. In females of all study arms (F(1)C, F(1)T140, and F(3)T21) an early onset of aberrant estrous cycles, suggesting early reproductive senescence, was observed in the 500 ppm groups. In the F(3)T21 arm, there were also significant effects on the onset of aberrant estrous cycles in the 5 and 100 ppm groups. Pituitary gland weights were significantly increased in females in the 500 ppm groups of the F(1)C and F(1)T140 study arms and in the 100 ppm group of the F(3)T21 arm. In F(1)C females, there was a significant positive trend in the incidences of mammary gland adenoma or adenocarcinoma (combined) regardless of whether an unmodified or natural log-transformed dose scale was used in the analysis, and the incidence in the 500 ppm group was significantly greater than that in the control group. A significant negative trend occurred in the incidences of benign mammary gland fibroadenoma in F(1)C females, and the incidence in the 500 ppm group was significantly less than that in the control group. In 5 and 100 ppm F(1)T140 females, the combined incidences of adenoma and adenocarcinoma were less than those in the control or 500 ppm groups, although these were not statistically significant differences. When the natural log-transformed dose scale was used, a marginally significant positive trend occurred in the incidences of adenoma or adenocarcinoma (combined) in F(3)T21 females. There were positive trends in the incidences of adenoma or carcinoma (combined) in the pars distalis of the pituitary gland of females in the F(1)C and F(1)T140 arms, and the incidence in the 500 ppm group was significantly greater than that in the controls in the F(1)C study arm. In F(1)C males, a significant positive trend (unmodified dose scale only) occurred in the incidences of combined adenoma or carcinoma of the pancreatic islets. While the incidence in the 500 ppm group was elevated relative to that in the control group (6/49 versus 1/49), this was not statistically significant. The fact that transitional lesions (i.e., hyperplasia) were not observed combined with variable control rates in males of this substrain of rats led to the conclusion that this lesion was not likely to be related to genistein treatment.

Conclusions: Under the conditions of this 2-year feed study with continuous exposure to the test compound from conception through termination (F(1)C), there was no evidence of carcinogenic activity of genistein in male Sprague-Dawley rats exposed to 5, 100, or 500 ppm. There was some evidence of carcinogenic activity of genistein in female Sprague-Dawley rats based on increased incidences of mammary gland adenoma or adenocarcinoma (combined) and pituitary gland neoplasms. The incidence of benign mammary gland fibroadenoma in female rats was significantly decreased in the 500 ppm group. Under the conditions of this 2-year feed study with exposure to the test compound from conception through 20 weeks followed by control feed until termination (F(1)T140), there was no evidence of carcinogenic activity of genistein in male Sprague-Dawley rats exposed to 5, 100, or 500 ppm. There was equivocal evidence of carcinogenic activity of genistein in female Sprague-Dawley rats based on marginally increased incidences of pituitary gland neoplasms. Under the conditions of this 2-year feed study where offspring of three prior generations of animals exposed to the test compound were exposed from conception through weaning (PND 21) followed by control feed until termination (F(3)T21), there was no evidence of carcinogenic activity of genistein in male Sprague-Dawley rats exposed to 5, 100, or 500 ppm. There was equivocal evidence of carcinogenic activity of genistein in female Sprague-Dawley rats based on increased incidences of mammary gland adenoma or adenocarcinoma (combined). Exposure to genistein was also shown to accelerate the onset of aberrant estrous cycles in female Sprague-Dawley rats whether exposures were continuous or truncated at PND 140 or at weaning. The effects of genistein on estrous cycling and the incidences of common hormonally related spontaneous neoplasms of female Sprague-Dawley rats are consistent with an estrogenic mechanism of toxicity.

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染料木素(casno . 446-72-0)对Sprague-Dawley大鼠的毒理学和致癌作用研究(饲料研究)。
未标记: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标相互作用。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。食用大豆和染料木黄酮对动物和人类有多种有益影响,但染料木黄酮的潜在不利影响也引起了关注,特别是生殖毒性和诱导或加强致癌作用,这主要是由于其雌激素活性较弱。由于这些担忧,染料木素被选为一种化合物进行研究,使用一种方案来评估多代和长期暴露于雌性激素制剂的影响,雌性激素制剂会在发育暴露的Sprague-Dawley大鼠幼鼠中产生细微的生殖道损伤。这里报告了为期2年的研究结果,并单独报告了多代生殖毒理学饲料研究的结果(国家毒理学规划,2008a)。来自初步剂量范围测定饲料研究(NTP, 2007)的数据使用高达1,250 ppm的暴露浓度来选择本研究中0、5、100和500 ppm的膳食暴露浓度。多代生殖毒理学研究检查了F(0)至F(4)代,F(5)窝在断奶时终止,重点关注生殖终点(NTP, 2008a)。动物从F(0)代6周龄开始暴露至F(3)代断奶,F(0)至F(4)代动物在20周龄尸检。目前的研究是一项为期2年的饮食研究,使用了三个暴露组:从怀孕到2年的持续暴露(指定F(1)连续,或F(1)C),从怀孕到20周的暴露,然后进行对照饮食,直到2年[指定F(1)在产后140天(PND)截断,或F(1)T140],以及从怀孕到断奶,然后进行对照饮食,直到2年(指定F(3)在PND 21天截断,或F(3)T21)。F(3)T21臂的“F(3)”标识表明,这些动物是多代生殖毒理学研究中F(3)动物的兄弟姐妹(NTP, 2008a)。F(1)C和F(1)T140动物也是兄弟姐妹,但它们来自一个单独的育种,与多代生殖毒理学研究中用于产生F(1)代的程序相同。本研究中的动物在其生命的不同阶段(从受孕到2岁终止)暴露于染料木素,并且在研究过程中摄入的剂量不同。在怀孕期间,水坝的摄入剂量约为每天0、0.5、9或45毫克/公斤体重。在哺乳期,母鼠每天摄入的剂量分别为0、0.7、15和75 mg/kg。在多代生殖毒理学研究中描述的补充研究表明,染料木素通过母鼠的乳汁向幼崽转移的可能性很小。在PND 140之前,女性每天直接摄入的染料木素平均剂量约为0.4、8或44 mg/kg,男性每天摄入的染料木素平均剂量为0.4、7或37 mg/kg。在PND 140至研究结束期间,女性的平均摄入剂量约为每天0.3、5或29 mg/kg,男性为每天0.2、4或20 mg/kg。在目前的研究中,每个性别的50只动物最初被分配到研究的每个分支的每个暴露组。在对照组中,另外一到四只被指定为哨兵的动物的组织病理学数据也包括在分析和报告中,这些动物已经死亡或过早死亡。所有对照组和暴露组的存活率相似,男性的存活率为62%至86%,女性为43%至64%。在整个研究过程中,500ppm F(1)C女性的平均体重低于对照组。在整个研究过程中,500ppm F(1)T140大鼠的平均体重低于对照组。在所有研究组(F(1)C, F(1)T140和F(3)T21)中,在500ppm组中观察到异常发情周期的早期发作,表明早期生殖衰老。在F(3)T21组中,5 ppm和100 ppm组对异常发情周期的发生也有显著影响。在F(1)C和F(1)T140研究组的500 ppm组和F(3)T21研究组的100 ppm组中,女性脑垂体重量显著增加。在F(1)C女性中,无论在分析中使用的是未修改剂量表还是自然对数转换剂量表,乳腺腺瘤或腺癌(合并)的发病率都有显著的正趋势,且500 ppm组的发病率明显大于对照组。 F(1)C女性乳腺良性纤维腺瘤的发病率呈显著负相关,且500 ppm组的发病率明显低于对照组。在5和100 ppm F(1)T140的女性中,腺瘤和腺癌的总发病率低于对照组或500 ppm组,尽管这些差异在统计学上没有显著性差异。当使用自然对数转化剂量量表时,F(3)T21女性中腺瘤或腺癌(合并)的发病率呈微弱显著的阳性趋势。F(1)C组和F(1)T140组女性垂体远端部腺瘤或癌(合并)的发病率呈上升趋势,其中500 ppm组的发病率显著高于F(1)C组的对照组。在F(1)C男性中,合并腺瘤或胰岛癌的发生率有明显的阳性趋势(仅未修改剂量量表)。虽然500ppm组的发病率相对于对照组升高(6/49 vs 1/49),但这在统计学上并不显著。在这一亚系的雄性大鼠中,没有观察到过渡性病变(即增生),再加上不同的控制率,因此得出结论,这种病变不太可能与染料木黄酮治疗有关。结论:在这项为期2年的饲料研究中,从受孕到终止(F(1)C)持续暴露于试验化合物,在暴露于5ppm、100 ppm或500ppm的雄性Sprague-Dawley大鼠中,没有证据表明染料木素具有致癌活性。雌性sd大鼠乳腺腺瘤或腺癌(合并)和垂体瘤的发病率增加,表明染料木素在雌性sd大鼠中有致癌活性。500ppm组雌性大鼠乳腺良性纤维腺瘤的发生率明显降低。在这项为期2年的饲料研究条件下,从受孕到20周暴露于试验化合物,然后用对照饲料直到终止(F(1)T140),在暴露于5ppm、100 ppm或500ppm的雄性Sprague-Dawley大鼠中,没有证据表明染料木素具有致癌活性。在雌性Sprague-Dawley大鼠中,染料木素致癌活性的证据是模棱两可的,这是基于脑垂体肿瘤发生率的轻微增加。在这项为期2年的饲料研究中,前三代动物的后代从受孕到断奶(PND 21)一直暴露在试验化合物中,然后是对照饲料,直到终止(F(3)T21),在暴露于5ppm、100 ppm或500ppm的雄性Sprague-Dawley大鼠中,没有证据表明染料木素具有致癌活性。基于乳腺腺瘤或腺癌(合并)发生率的增加,染料木素在雌性Sprague-Dawley大鼠中致癌活性的证据模棱两可。暴露于染料木素也被证明会加速雌性Sprague-Dawley大鼠异常发情周期的开始,无论暴露是连续的还是在PND 140或断奶时被截断。染料木素对雌性Sprague-Dawley大鼠发情周期和常见激素相关自发性肿瘤发生率的影响与雌激素毒性机制一致。
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