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5,5-二苯基乙内酰脲(CAS编号:57-41-0)(苯妥英)在F344/N大鼠和B6C3F1小鼠中的毒理学和致癌性研究(饲料研究)

Toxicology and Carcinogenesis Studies of 5,5-Diphenylhydantoin (CAS No. 57-41-0) (Phenytoin) in F344/N Rats and B6C3F1 Mice (Feed Studies).

出版信息

Natl Toxicol Program Tech Rep Ser. 1993 Nov;404:1-303.

Abstract

5,5-Diphenylhydantoin and its sodium salt are primarily used in the treatment of grand mal and psychomotor seizures, often in combination with other anticonvulsants, including phenobarbital. 5,5-Diphenylhydantoin is a suspected human carcinogen and was one of three compounds selected by the NTP to investigate the potential value of perinatal exposures in assessing chemical carcinogenicity. Chronic toxicity and carcinogenicity studies of 5,5-diphenylhydantoin were conducted in male and female F344/N rats and B6C3F1 mice. The studies were designed to determine the following: a) the effects of 5,5-diphenylhydantoin in the diet given to rats and mice during the adult (F1) period only (a typical carcinogenicity study), b) the toxic and carcinogenic effects of 5,5-diphenylhydantoin in rats and mice receiving perinatal (F0) exposure only (dietary exposure of dams prior to breeding and throughout gestation and lactation), and c) the effects of combined perinatal and adult exposure to 5,5-diphenylhydantoin. Genetic toxicology studies were conducted in Salmonella typhimurium, mouse Iymphoma cells, cultured Chinese hamster ovary cells, Drosophila melanogaster, and mouse bone marrow cells. STUDIES IN F344/N RATS: A 13-week toxicity study was conducted to select the exposure levels for adults in the 2-year study. The exposure levels for the 13-week study ranged from 300 to 4,800 ppm 5,5-diphenylhydantoin in the diet. The final mean body weights of males and females exposed to 2,400 or 4,800 ppm were significantly decreased. All groups showed a net weight gain over the study period, although the mean body weight gain of females in the 4,800 ppm group was only one-half that of the controls. Feed consumption also decreased with increasing exposure level. No chemical-related gross lesions were present in the tissues of exposed rats. Microscopically, centrilobular hypertrophy of hepatocytes was observed in the liver of rats in the 4,800 ppm groups. Based on these results, 2,400 ppm was selected as the highest exposure for the adult-only portion of the 2-year carcinogenicity study. A gestational study was performed to select the exposure levels for the perinatal portion of the 2-year study. The exposure levels ranged from 80 to 2,400 ppm 5,5-diphenylhydantoin in the diet of the dams. The 2,400 ppm exposure level was found to have reproductive and embryotoxic effects, as none of the sperm-positive females delivered litters. In the 800 ppm group, a greater number of pups died between postnatal day 1 and day 28 than in the control group. No gross external malformations were observed among fetuses or pups surviving to term in any exposure group, and no gross or histopathologic lesions were observed in the animals exposed to 800 ppm for 4 weeks following weaning. Based on these results, 630 ppm was selected as the highest exposure level for the perinatal portion of the 2-year carcinogenicity study. The eight F0:F1 exposure combinations selected for the 2-year study are listed in the table (contained in full report - page 6). In the 2-year study, male and female rats in the 630:2,400 ppm groups evaluated at 9 months had increased relative liver weights. Hematologic evaluations indicated mild but consistent chemical-related increases in erythrocyte and platelet counts in male and female rats. Mild decreases in triglyceride concentrations and alanine aminotransferase enzyme activity were seen generally in the high-exposure groups. In the 2-year study, the survival of exposed rats was similar to that of the controls. However, body weights of exposed rats were lower than those of the controls, and body weights were 11% to 35~ lower in rats receiving adult exposure of 2,400 ppm 5,5-diphenylhydantoin. Feed consumption was similar for exposed and control groups. Hepatocellular neoplasms, primarily adenomas, occurred with a positive trend in male rats fed 5,5-diphenylhydantoin only as adults (0:0 ppm, 0/50; 0:800 ppm, 2/50; 0:2,400 ppm, 4/50). There were no increased neoplasm incidences at other sites in exposed males or at any site in exposed females.emales. Perinatal-only or combined perinatal and adult exposure to 5,5-diphenylhydantoin did not enhance the overall incidences of liver neoplasms in male or female rats. However, the finding of 5/49 hepatocellular adenomas in the 630:2,400 male rat group was consistent with the marginally elevated liver neoplasm rate observed in the 0:2,400 group. Decreased incidences of a number of different neoplasms in exposed groups were most likely related to the lower body weights. STUDIES IN B6C3F1 MICE: A 13-week toxicity study was conducted to select the exposure levels for adults in the 2-year study. The exposure levels for the 13-week study ranged from 75 to 1,200 ppm 5,5-diphenylhydantoin in the diet. With the exception of one male, all mice exposed to 1,200 ppm died before the end of the study. No other chemical-related deaths occurred. All groups of mice except the 1,200 ppm groups gained weight over the 13-week period; however, an exposure related decrease in body weight gain was seen in males and females. Feed consumption by exposed and control groups was generally similar. Chemical related histomorphologic lesions were present in the liver of exposed mice, particularly 600 ppm males, and consisted of centrilobular hypertrophy of hepatocytes. Females appeared to be less sensitive than males to the effects of 5,5-diphenylhydantoin on growth and on histomorphologic liver lesions. Based on these results, 300 ppm (males) and 600 ppm (females) were selected as the highest exposure levels for the adult-only portion of the 2-year carcinogenicity study. A gestational study was performed to select the exposure levels for the perinatal portion of the 2-year study. The exposure levels for males and females ranged from 20 to 600 ppm 5,5-diphenylhydantoin in the diet. In general, reproductive performance and maternal care were poor in all groups, including the controls, thus restricting the sample size and sensitivity of this evaluation. There were no litters in the 600 ppm group, and maternal weight gain was depressed. There were no gross external malformations among pups surviving to term, and no gross or histopathologic lesions were observed in any mice exposed for 4 weeks following weaning. Based on these results, 210 ppm was selected as the highest exposure level for the perinatal portion of the 2-year carcinogenicity study. The F0:F1 exposure combinations selected for the 2-year study are listed in the following table (contained in full report - page 7). For mice evaluated at 9 months, males and females receiving the highest F0:F1 exposure levels had increased relative liver weights. In the 2-year study, the survival of exposed animals was similar to that of the controls; however, body weights were lower for exposed groups, and decreased body weights were most severe in adult females receiving 600 ppm 5,5-diphenylhydantoin. Feed consumption was similar for exposed and control groups. The incidences of hepatocellular neoplasms were increased in female mice receiving adult-only exposure (0:0 ppm, 5/48; 0:200 ppm, 14/49; 0:600 ppm, 30/50) or combined perinatal and adult exposure (210:200 ppm, 16/50; 210:600 ppm, 34/50). A marginally increased incidence of liver neoplasms (12/49) occurred in females in the perinatal-only (210:0) exposure group. There were no chemical-related increased incidences of liver neoplasms in males receiving adult-only or perinatal-only exposure. However, males receiving the high-exposure combined perinatal and adult exposure regimen (210:300 ppm) had an increased incidence of liver neoplasms (41/50) compared to the 0:0 (29/50), 0:300 (26/49), and 210:0 (33/50) groups. As a result, there was a significant enhancement (interaction) associated with combined perinatal and adult exposure. Such enhancement of neoplasia did not occur in female mice. Decreased incidences of malignant neoplasms in exposed groups were most likely related to the lower body weights. GENETIC TOXICOLOGY: In general, tests for genotoxic activity of 5,5-diphenylhydantoin were negative. All in vitro testing was performed in the presence and the absence of exogenous metabolic activation (S9). 5,5-Diphenylhydantoin did not induce mutations in Salmonella typhimurium, in L5178Y mouse Iymphoma cells, or in germ cells of male Drosophila melanogaster, nor did it induce chromosomal aberrations in cultured Chinese hamster ovary cells. A small but statistically significant increase was obtained in the cultured Chinese hamster ovary cell test for induction of sister chromatid exchanges in the presence of S9; without S9, no increase in sister chromatid exchanges was observed. In vivo, 5,5-diphenylhydantoin did not induce micronuclei polychromatic erythrocytes or chromosomal aberrations in bone marrow cells of male mice; equivocal results were obtained in an in vivo test for induction of sister chromatid exchanges in mouse bone marrow cells. CONCLUSIONS: Adult-Only Exposure: Under the conditions of these 2-year, adult-only, dietary exposure studies, there was equivocal evidence of carcinogenic activity of 5,5-diphenylhydantoin in male F344/N rats based on marginally increased incidences of hepatocellular neoplasms. There was no evidence of carcinogenic activity of 5,5-diphenylhydantoin in female F344/N rats given 240, 800, or 2,400 ppm. There was no evidence of carcinogenic activity of 5,5-diphenylhydantoin in male B6C3F1 mice given 30,100, or 300 ppm. There was clear evidence of carcinogenic activity of 5,5-diphenylhydantoin in female B6C3F1 mice based on increased incidences of hepatocellular neoplasms. Perinatal-Only Exposure: Perinatal exposure alone (through dietary administration of 210 ppm 5,5-diphenylhydantoin during the perinatal period) caused a marginal increase in the incidences of hepatocellular neoplasms in female B6C3F1 mice evaluated 2 years after cessation of exposure. In male and female F344/N rats, exposure to 630 ppm during the perinatal period did not influence the incidences of hepatocellular or other neoplasms. Similarly, exposure of male B6C3F1 mice to dietary levels of 210 ppm 5,5-diphenylhydantoin during the perinatal period did not affect neoplasm incidences. No teratologic effects were observed. Combined Perinatal and Adult Exposure: Combined perinatal and adult dietary exposure to 5,5-diphenylhydantoin confirmed the findings of the increased incidences of hepatocellular neoplasms for adult-only exposures in male F344/N rats and female B6C3F1 mice, although combined exposure did not enhance these neoplastic effects. However, in male B6C3F1 mice, combined perinatal and adult exposure resulted in increased incidences of hepatocellular neoplasms (hepatocellular carcinomas and multiple adenomas) that were not seen when dietary exposure was limited to the adult exposure period only. Synonyms: Diphenylhydantoin; 5,5-diphenyl-2,4-imidazolidinedione Trade names: Difhydan; Dihycon; Di-Hydan; Di-Lan; Dilabid; Dilantin; Ekko; Hydantol; Lehydan; Zentropil

摘要

5,5-二苯基乙内酰脲及其钠盐主要用于治疗癫痫大发作和精神运动性发作,通常与其他抗惊厥药联合使用,包括苯巴比妥。5,5-二苯基乙内酰脲是一种疑似人类致癌物,是美国国家毒理学计划(NTP)选定的三种化合物之一,用于研究围产期暴露在评估化学致癌性方面的潜在价值。对雄性和雌性F344/N大鼠以及B6C3F1小鼠进行了5,5-二苯基乙内酰脲的慢性毒性和致癌性研究。这些研究旨在确定以下内容:a)仅在成年期(F1)给大鼠和小鼠喂食含5,5-二苯基乙内酰脲的饲料所产生的影响(典型的致癌性研究),b)仅在围产期(F0)给大鼠和小鼠喂食5,5-二苯基乙内酰脲所产生的毒性和致癌作用(在繁殖前、整个妊娠期和哺乳期给母鼠喂食),以及c)围产期和成年期联合暴露于5,5-二苯基乙内酰脲的影响。在鼠伤寒沙门氏菌、小鼠淋巴瘤细胞、培养的中国仓鼠卵巢细胞、黑腹果蝇和小鼠骨髓细胞中进行了遗传毒理学研究。

F344/N大鼠研究:进行了一项为期13周的毒性研究,以选择两年研究中成年大鼠的暴露水平。为期13周的研究中,饲料中5,5-二苯基乙内酰脲的暴露水平为300至4800 ppm。暴露于2400或480 ppm的雄性和雌性大鼠的最终平均体重显著下降。所有组在研究期间体重均有净增加,尽管4800 ppm组雌性大鼠的平均体重增加仅为对照组的一半。随着暴露水平的增加,饲料消耗量也减少。在暴露大鼠的组织中未发现与化学物质相关的肉眼可见病变。显微镜检查发现,4800 ppm组大鼠肝脏中出现中央小叶肝细胞肥大。基于这些结果,选择2400 ppm作为两年致癌性研究中仅成年大鼠部分的最高暴露水平。进行了一项妊娠期研究,以选择两年研究中围产期部分的暴露水平。母鼠饲料中5,5-二苯基乙内酰脲的暴露水平为80至2400 ppm。发现2400 ppm的暴露水平具有生殖和胚胎毒性作用,因为没有精子阳性的雌性大鼠产仔。在800 ppm组中,出生后第1天至第28天死亡的幼崽数量比对照组多。在任何暴露组中,存活至足月的胎儿或幼崽均未观察到明显的外部畸形,断奶后暴露于800 ppm 4周的动物也未观察到明显的肉眼或组织病理学病变。基于这些结果,选择630 ppm作为两年致癌性研究中围产期部分的最高暴露水平。为两年研究选择的八个F0:F1暴露组合列于表中(完整报告第6页)。在两年研究中,9个月时评估的630:2400 ppm组的雄性和雌性大鼠肝脏相对重量增加。血液学评估表明,雄性和雌性大鼠的红细胞和血小板计数出现轻微但持续的与化学物质相关的增加。高暴露组中甘油三酯浓度和丙氨酸转氨酶活性普遍略有下降。在两年研究中,暴露大鼠的存活率与对照组相似。然而,暴露大鼠的体重低于对照组,接受成年期2400 ppm 5,5-二苯基乙内酰脲暴露的大鼠体重低11%至35%。暴露组和对照组的饲料消耗量相似。仅在成年期喂食5,5-二苯基乙内酰脲的雄性大鼠(0:0 ppm,0/50;0:800 ppm,2/50;0:2400 ppm,4/50)中,肝细胞肿瘤(主要是腺瘤)的发生率呈上升趋势。暴露雄性大鼠的其他部位或暴露雌性大鼠的任何部位肿瘤发生率均未增加。仅围产期或围产期与成年期联合暴露于5,5-二苯基乙内酰脲并未增加雄性或雌性大鼠肝脏肿瘤的总体发生率。然而,630:2400雄性大鼠组中发现5/49例肝细胞腺瘤,与0:2400组中观察到的肝脏肿瘤发生率略有升高一致。暴露组中多种不同肿瘤的发生率降低很可能与体重较低有关。

B6C3F1小鼠研究:进行了一项为期13周的毒性研究,以选择两年研究中成年小鼠的暴露水平。为期13周的研究中,饲料中5,5-二苯基乙内酰脲的暴露水平为75至1200 ppm。除一只雄性小鼠外,所有暴露于1200 ppm的小鼠在研究结束前死亡。未发生其他与化学物质相关的死亡。除1200 ppm组外,所有小鼠组在13周内体重均增加;然而,雄性和雌性小鼠的体重增加均出现与暴露相关的下降。暴露组和对照组的饲料消耗量总体相似。暴露小鼠的肝脏出现与化学物质相关的说组织形态学病变,特别是600 ppm组的雄性小鼠,表现为中央小叶肝细胞肥大。雌性小鼠似乎对5,5-二苯基乙内酰脲对生长和肝脏组织形态学病变的影响不如雄性小鼠敏感。基于这些结果,选择300 ppm(雄性)和600 ppm(雌性)作为两年致癌性研究中仅成年小鼠部分的最高暴露水平。进行了一项妊娠期研究,以选择两年研究中围产期部分的暴露水平。雄性和雌性小鼠的暴露水平为饲料中20至600 ppm 5,5-二苯基乙内酰脲。总体而言,所有组(包括对照组)的生殖性能及母性护理均较差,从而限制了该评估的样本量和敏感性。600 ppm组没有产仔,母鼠体重增加受到抑制。存活至足月的幼崽未出现明显的外部畸形,断奶后暴露4周的任何小鼠均未观察到明显的肉眼或组织病理学病变。基于这些结果,选择210 ppm作为两年致癌性研究中围产期部分的最高暴露水平。为两年研究选择的F0:F1暴露组合列于下表(完整报告第7页)。对于9个月时评估的小鼠,接受最高F0:F1暴露水平的雄性和雌性小鼠肝脏相对重量增加。在两年研究中,暴露动物的存活率与对照组相似;然而,暴露组的体重较低,接受600 ppm 5,5-二苯基乙内酰脲的成年雌性小鼠体重下降最为严重。暴露组和对照组的饲料消耗量相似。仅成年期暴露(0:0 ppm,5/48;0:200 ppm,14/49;0:600 ppm,30/50)或围产期与成年期联合暴露(210:200 ppm,16/50;210:600 ppm,34/50)的雌性小鼠肝细胞肿瘤发生率增加。仅围产期暴露组(210:0)的雌性小鼠肝脏肿瘤发生率略有增加(12/49)。仅成年期或仅围产期暴露的雄性小鼠肝脏肿瘤发生率未出现与化学物质相关的增加。然而,与0:0(29/50)、0:300(26/49)和210:0(33/50)组相比,接受高暴露围产期与成年期联合暴露方案(210:300 ppm)的雄性小鼠肝脏肿瘤发生率增加(41/50)。因此,围产期与成年期联合暴露存在显著增强(相互作用)。雌性小鼠未出现这种肿瘤形成增强现象。暴露组恶性肿瘤发生率降低很可能与体重较低有关。

遗传毒理学

总体而言,5,5-二苯基乙内酰脲的遗传毒性活性测试结果为阴性。所有体外测试均在有和没有外源性代谢激活(S9)的情况下进行。5,5-二苯基乙内酰脲在鼠伤寒沙门氏菌、L5178Y小鼠淋巴瘤细胞或雄性黑腹果蝇生殖细胞中未诱导突变,在培养的中国仓鼠卵巢细胞中也未诱导染色体畸变。在有S9的情况下,培养的中国仓鼠卵巢细胞测试中诱导姐妹染色单体交换出现小幅但具有统计学意义的增加;没有S9时,未观察到姐妹染色单体交换增加。在体内,5,5-二苯基乙内酰脲未在雄性小鼠骨髓细胞中诱导微核多色红细胞或染色体畸变;在小鼠骨髓细胞中诱导姐妹染色单体交换的体内测试结果不明确。

结论

仅成年期暴露:在这些为期两年的仅成年期饮食暴露研究条件下,基于肝细胞肿瘤发生率略有增加,有不明确的证据表明5,5-二苯基乙内酰脲对雄性F344/N大鼠具有致癌活性。给雌性F344/N大鼠喂食240、800或2400 ppm时,没有证据表明5,5-二苯基乙内酰脲具有致癌活性。给雄性B6C3F1小鼠喂食30、100或300 ppm时,没有证据表明5,5-二苯基乙内酰脲具有致癌活性。基于肝细胞肿瘤发生率增加,有明确的证据表明5,5-二苯基乙内酰脲对雌性B6C3F1小鼠具有致癌活性。仅围产期暴露:仅围产期暴露(在围产期通过饮食给予210 ppm 5,5-二苯基乙内酰脲)导致停止暴露两年后评估的雌性B6C3F1小鼠肝细胞肿瘤发生率略有增加。在雄性和雌性F344/N大鼠中,围产期暴露于630 ppm不会影响肝细胞或其他肿瘤的发生率。同样,围产期给雄性B6C3F1小鼠喂食210 ppm 5,5-二苯基乙内酰脲不会影响肿瘤发生率。未观察到致畸作用。围产期与成年期联合暴露:围产期与成年期联合饮食暴露于5,5-二苯基乙内酰脲证实了雄性F344/N大鼠和雌性B6C3F1小鼠仅成年期暴露时肝细胞肿瘤发生率增加的结果,尽管联合暴露并未增强这些肿瘤效应。然而,在雄性B6C3F1小鼠中,围产期与成年期联合暴露导致肝细胞肿瘤(肝细胞癌和多个腺瘤)发生率增加,而仅在成年期饮食暴露时未观察到这种情况。

同义词

二苯基乙内酰脲;5,5-二苯基-2,4-咪唑烷二酮

商品名

Difhydan;Dihycon;Di-Hydan;Di-Lan;Dilabid;Dilantin;Ekko;Hydantol;Leydan;Zentropil

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