Ganiger S, Malleshappa H N, Krishnappa H, Rajashekhar Geetha, Ramakrishna Rao V, Sullivan Frank
Toxicology Department, Rallis Research Centre, Rallis India Limited, Post Box No. 5813, Plot Nos. 21 and 22, Peenya II Phase, Bangalore 560 058, India.
Food Chem Toxicol. 2007 Jan;45(1):64-9. doi: 10.1016/j.fct.2006.07.016. Epub 2006 Aug 7.
The reproductive toxicity of curcumin, turmeric yellow, in Wistar rats was studied in order to generate additional relevant toxicity information for the use of curcumin in humans by oral administration. The two generation reproduction study was designed and conducted in accordance with OECD Guideline No. 416 [OECD, 1983. Guidelines for Testing of Chemicals, Guideline No. 416. Two Generation Reproduction Toxicity Study, adopted on 26th May 1983] and in compliance with Good Laboratory Practices (OECD, 1997 Principles of Good Laboratory Practice for the Testing of Chemicals. OECD, C(97)186/Final). The curcumin, mixed in the experimental diet at the concentrations of 1500, 3000 and 10,000 ppm was fed to three groups of rats, i.e., low, mid and high dose groups, and studied for two successive generations. A concurrent control group received experimental diet without the curcumin mixture. There were no treatment related adverse toxicological effects in the parental animals. No gross or microscopic changes were observed in any of the organs. None of the reproductive parameters were affected and there were no effects on the offspring other than a small reduction in pre-weaning body weight gain of the F2 pups at the highest dose level. It was concluded that the no observed adverse effect level (NOAEL) for reproductive toxicity of curcumin, fed in the diet for two successive generations to rats in this study was 10,000 ppm, which is equivalent to 847 and 959 mg/kg bodyweight (bw) per day for male rats and 1043 and 1076 for females for F0 and F1 generations, respectively. This study was the final toxicology study on curcumin reviewed by the Joint FAO/WHO Expert Committee on Food Additives (JECFA) at the 61st Meeting, 2003. The JECFA group considered that the small body weight reduction in the F2 pups of the highest dose group prevented this from being regarded as a no adverse effect level, and so allocated an ADI for curcumin of 0-3 mg/kg bw based on the intake of 250-320 mg/kg bw in the mid-dose group as the NOEL.
为了获取更多关于姜黄素经口服途径供人类使用的相关毒性信息,研究了姜黄素(姜黄)对Wistar大鼠的生殖毒性。两代繁殖研究按照经合组织(OECD)第416号指南[经合组织,1983年。化学品测试指南,第416号指南。两代繁殖毒性研究,1983年5月26日采用]设计并开展,并符合良好实验室规范(经合组织,1997年化学品测试良好实验室规范原则。经合组织,C(97)186/Final)。将姜黄素以1500、3000和10000 ppm的浓度混入实验饲料中,分别喂给三组大鼠,即低、中、高剂量组,并连续研究两代。一个同期对照组给予不含姜黄素混合物的实验饲料。亲代动物未出现与处理相关的不良毒理学效应。任何器官均未观察到大体或微观变化。所有生殖参数均未受影响,除了最高剂量组F2幼崽断奶前体重增加略有减少外,对后代也无影响。得出结论,在本研究中,连续两代经饲料喂给大鼠的姜黄素生殖毒性的未观察到有害作用水平(NOAEL)为10000 ppm,相当于F0代雄性大鼠和雌性大鼠每天分别为847和959 mg/kg体重(bw),F1代雄性大鼠和雌性大鼠分别为1043和1076 mg/kg bw。本研究是联合国粮食及农业组织/世界卫生组织食品添加剂联合专家委员会(JECFA)在2003年第61次会议上审查的关于姜黄素的最终毒理学研究。JECFA小组认为,最高剂量组F2幼崽体重略有减轻,因此不能将此视为无不良作用水平,所以根据中剂量组250 - 320 mg/kg bw的摄入量作为无观察到有害作用水平(NOEL),为姜黄素分配了0 - 3 mg/kg bw的每日允许摄入量(ADI)。