Deoxynivalenol and Nivalenol (2nd edition) [Assuring the Maximum Level of Deoxynivalenol in Wheat] (Natural Toxins and Mycotoxins).

Food safety (Tokyo, Japan) Pub Date : 2020-12-25 eCollection Date: 2020-12-01 DOI:10.14252/foodsafetyfscj.D-20-00031
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引用次数: 1

Abstract

Food Safety Commission of Japan (FSCJ) was requested by the Ministry of Health, Labour and Welfare (MHLW) to conduct a risk assessment of deoxynivalenol (DON) to assure the maximal level for DON in foods. Previously, FSCJ had conducted a self-tasking risk assessment of DON and nivalenol (NIV) in 2010. In the current 2nd edition, only the assessment of DON has been revised. Grains contaminated with DON may be also contaminated with its derivatives, namely, 3-acetyldeoxynivalenol (3-Ac-DON), 15-acetyldeoxynivalenol (15-Ac-DON) and deoxynivalenol-3-glucoside (DON-3-glucoside). However, these substances orally ingested are rapidly biotransformed into DON. Therefore, FSCJ identified the total DON (sum of DON and its derivatives) to be assessed. The toxicity of DON was assessed based on the data of absorption-distribution-metabolism-excretion (ADME), acute toxicity, sub-acute toxicity, chronic toxicity, carcinogenicity, reproductive/developmental toxicity, genotoxicity, and immunotoxicity. DON was considered to have no significant genotoxic activity in vivo. The no-observed-adverse-effect level (NOAEL), based on the two-year chronic toxicity study in mice, was set at 0.1 mg DON/kg bw/day. By applying an uncertainty factor (UF) of 100, the TDI for DON was determined as 1 µg /kg bw/day. The average estimated exposure levels of total DON were 0.09 µg /kg bw/day and 0.22 µg/kg bw/day in the whole population and the 1-6 years group, respectively, by the Monte-Carlo method. The average exposure level in Japan was thus judged to be below the TDI, although a chance to exceed the TDI remains possible in the 1-6 years group depending on eating habits and DON contamination. For NIV, the genotoxic property was not able to be assessed due to the limited availability of the experimental data. No carcinogenic effect was observed in a two-year chronic toxicity study in mice, and the International Agency for Research on Cancer (IARC) also classifies Fusarium spp toxins including NIV to be in group 3. FSCJ thus judged that TDI can be set for NIV. Based on various toxicity studies, the TDI of NIV was determined at 0.4 µg/kg bw/day by taking into account of LOAEL 0.4 mg NIV/kg bw/day in a subacute toxicity study in rats with 90-day oral administration and UF of 1,000. The exposure level of NIV in Japan was estimated to be below the TDI. FSCJ judged it's unlikely that NIV intake leads to adverse health effects in general population.

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脱氧雪腐镰刀菌醇和雪腐镰刀菌醇(第2版)[确保小麦中脱氧雪腐镰刀菌醇的最高水平](天然毒素和真菌毒素)。
日本卫生、劳动和福利部(MHLW)要求食品安全委员会(FSCJ)对脱氧雪腐镰刀菌醇(DON)进行风险评估,以确保食品中DON的最高水平。此前,FSCJ于2010年进行了DON和nivalol (NIV)的自我任务风险评估。在目前的第2版中,只修改了DON的评估。被DON污染的谷物也可能被其衍生物3-乙酰脱氧雪腐腐菌醇(3-Ac-DON)、15-乙酰脱氧雪腐腐菌醇(15-Ac-DON)和脱氧雪腐腐菌醇-3-葡萄糖苷(DON-3-葡萄糖苷)污染。然而,这些物质口服后会迅速生物转化为DON。因此,FSCJ确定了待评估的总DON (DON及其衍生物的总和)。根据吸收-分布-代谢-排泄(ADME)、急性毒性、亚急性毒性、慢性毒性、致癌性、生殖/发育毒性、遗传毒性和免疫毒性等指标评估DON的毒性。DON在体内被认为没有显著的遗传毒性活性。根据为期两年的小鼠慢性毒性研究,未观察到的不良反应水平(NOAEL)设定为0.1 mg DON/kg bw/day。采用不确定因子(UF)为100,确定DON的TDI为1µg /kg bw/day。通过蒙特卡罗方法估计,整个人群和1-6岁组的总DON平均暴露水平分别为0.09µg/kg bw/day和0.22µg/kg bw/day。因此,日本的平均暴露水平被判断为低于TDI,尽管1-6岁年龄组仍有可能超过TDI,这取决于饮食习惯和DON污染。对于NIV,由于实验数据的有限可用性,无法评估其遗传毒性。在一项为期两年的小鼠慢性毒性研究中没有观察到致癌作用,国际癌症研究机构(IARC)也将镰刀菌毒素包括NIV归为第3组。FSCJ由此判断TDI可以设置为NIV。根据各种毒性研究,在一项亚急性毒性研究中,大鼠口服90天,UF为1000,考虑LOAEL 0.4 mg NIV/kg bw/day,确定了NIV的TDI为0.4µg/kg bw/day。据估计,日本的NIV暴露水平低于TDI。FSCJ认为,在一般人群中,NIV的摄入不太可能导致不利的健康影响。
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