六价铬(污染物)。

Food safety (Tokyo, Japan) Pub Date : 2019-06-28 eCollection Date: 2019-06-01 DOI:10.14252/foodsafetyfscj.D-1900002
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引用次数: 5

摘要

日本食品安全委员会(FSCJ)对六价铬(以下简称Cr (VI))进行了风险评估,该评估与厚生劳动省制定的饮料标准修正案有关。Cr (VI)对实验动物的主要毒性是小肠损伤和贫血。在最低LOAEL下观察到的结果是小鼠十二指肠粘膜上皮弥漫性增生。在致癌性方面,饮用水处理Cr (VI)显著增加小鼠小肠和大鼠口腔黏膜和舌头肿瘤的发生率。因此,FSCJ认为Cr (VI)具有致癌性。Cr (VI)在体外和体内经肠外给药后的许多基因毒性研究中显示阳性结果,而口服给药后没有明显阳性结果。这些数据表明了铬(VI)的遗传毒性,尽管包括饮用水在内的口服给药的遗传毒性尚不清楚。小鼠小肠肿瘤的发生机制认为:长期暴露于Cr (VI)对小肠黏膜上皮的持续损伤,导致小肠隐窝增生,从而导致肿瘤的形成。在转基因大鼠和小鼠的体内基因突变实验中,在饮用水中暴露Cr (VI) 28天(大鼠)或90天(小鼠)后,致癌靶组织中转基因基因的突变频率均未见显著增加(1),2)。基于这些结果,FSCJ判断通过饮用水摄入Cr (VI)的致癌机制很难归因于遗传毒性。FSCJ认为,基于人群非职业暴露和职业暴露的流行病学研究结果,很难对饮用水中铬(VI)进行定量风险评估。因此,根据通过饮用水口服接触铬(VI)的动物研究结果,确定每日可耐受摄入量(TDI)是相当可行的。FSCJ对0.11 mg/kg bw/day的BMDL10应用不确定因子100确定了Cr (VI)的TDI为1.1 μg/kg bw/day,这是由于两年口服暴露研究中观察到的雄性小鼠十二指肠弥漫性上皮增生所致。由于食物中的铬被认为是三价铬(3),FSCJ估计每天从饮用矿泉水和自来水中摄入的铬(VI)。平均和高摄食量分别约为0.04 μg/kg bw/d和0.290 μg/kg bw/d。由于这两个值均低于TDI 1.1 μg/kg bw/day,因此FSCJ认为,在目前通过饮用矿泉水和自来水暴露的Cr (VI)对健康的影响风险极低。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Hexavalent chromium (Contaminants).

The Food Safety Commission of Japan (FSCJ) conducted a risk assessment of hexavalent chromium, hereinafter referred to as Cr (VI), related to the amendment of the standards for beverages established by the Ministry of Health, Labour and Welfare. Major toxicities induced by Cr (VI) were damages to small intestine and anemia in experimental animals. The finding observed at the lowest LOAEL was diffuse hyperplasia of mucosal epithelium in the duodenum in mice. Regarding to carcinogenicity, Cr (VI)-treatment by drinking water significantly increased incidences of tumors in the small intestine in mice and in the oral mucosa and tongue in rats. Therefore, FSCJ considered that Cr (VI) is carcinogenic. Cr (VI) showed positive results in many genotoxic studies in vitro, and in vivo after parenteral administration, whereas no clear positive results were obtained after the oral administration. These data indicate the genotoxic properties of Cr (VI), though genotoxicity by the oral administration including drinking water remains unclear. The mechanism of small intestinal tumors in mice is considered as follows: Continuous damage to mucosal epithelium in the small intestine by long-term exposure to Cr (VI) induces the hyperplasia in the crypt of small intestine, which would lead to the formation of tumor. In the in vivo gene mutation assays using transgenic rats and mice, no significant increases in mutant frequencies of the transgenes were observed in the carcinogenic target tissues, after exposure to Cr (VI) in drinking water for either 28 (rats) or 90 days (mice)1), 2). On the basis of these results, FSCJ judged that the carcinogenic mechanism of Cr (VI) intakes through drinking water was hardly attributable to the genotoxicity. FSCJ considered that the quantitative risk assessment of Cr (VI) through drinking water was difficult to conduct based on the results from epidemiological studies of non-occupational and occupational exposures in human population. Consequently, specifying a tolerable daily intake (TDI), based on the results of animal studies with oral exposure to Cr (VI) through drinking water, is rather feasible. FSCJ specified the TDI of Cr (VI) as 1.1 μg/kg bw/day after applying the uncertainty factor of 100 to BMDL10 of 0.11 mg/kg bw/day, which was ascribed on the diffuse epithelial hyperplasia in the duodenum in male mice observed in the two-year oral exposure study. Since chromium in food is regarded to be present as trivalent chromium3), FSCJ estimated daily intake of Cr (VI) from consumption of mineral water and tap water. The estimation gave the mean and high intakes as ca. 0.04 μg/kg bw/day and 0.290 μg/kg bw/day, respectively. Since both of these two values were lower than the TDI, 1.1 μg/kg bw/day, FSCJ concluded the risk of health effects from Cr (VI) at the current exposure through the consumption of mineral water and tap water to be extremely low.

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