{"title":"对低无机砷暴露的欧洲人口的健康风险没有明确的关切(概述)","authors":"Z. Šlejkovec, T. Bizjak, M. Horvat, I. Falnoga","doi":"10.1080/10807039.2022.2143319","DOIUrl":null,"url":null,"abstract":"Abstract An overview of recent European background inorganic arsenic (iAs) levels and related human health risks is given. The main aim was to summarize and confront the existing concentration data, unresolved low dose-response issues (linearity, nonlinearity, threshold, adaptation, hormesis), and methodological approaches hampered by several uncertainties on several levels. Daily doses are calculated from dietary intake (food, water As content multiplied by intake frequencies) and compared by reverse calculated doses from urine iAs metabolites (iAs + dimethylarsenic acid + monomethylarsonic acid) from human biomonitoring data (both in a range 0.05–0.60 μg kg−1 bw/day for children, adolescents and adults). With data obtained a health risk assessment is performed by existing regulation norms. 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引用次数: 2
摘要
摘要概述了最近欧洲背景无机砷(iAs)水平和相关的人类健康风险。主要目的是总结和面对现有的浓度数据,未解决的低剂量反应问题(线性,非线性,阈值,适应,激效),以及在几个层面上受到几个不确定因素阻碍的方法方法。每日剂量根据膳食摄入量(食物、水中砷含量乘以摄入频率)计算,并与人体生物监测数据中尿液砷代谢物(砷+二甲基larsenic酸+单甲基larsonic酸)的反向计算剂量进行比较(儿童、青少年和成人的剂量范围均为0.05-0.60 μg kg - 1 bw/天)。根据获得的数据,根据现有法规规范进行健康风险评估。解决了几个缺陷。例如,作为iAs代谢物的尿液DMA被高估了,因为它的来源也可能是食物。此外,现有的监管规范(正在由美国环境保护局重新评估)基于线性剂量反应方法,仅对高暴露有效,对低暴露水平非常可疑。然而,即使使用常规方法(存在讨论过的缺陷,导致预期的高估),根据人类生物监测数据计算的MOE(21.4),对于平均食物摄入量和饮食中平均iAs浓度(15.3-40.6)的被调查年龄组,潜在的癌症风险估计与暴露边际(MOE)有关。
No clear concerns related to health risks in the European population with low inorganic arsenic exposure (overview)
Abstract An overview of recent European background inorganic arsenic (iAs) levels and related human health risks is given. The main aim was to summarize and confront the existing concentration data, unresolved low dose-response issues (linearity, nonlinearity, threshold, adaptation, hormesis), and methodological approaches hampered by several uncertainties on several levels. Daily doses are calculated from dietary intake (food, water As content multiplied by intake frequencies) and compared by reverse calculated doses from urine iAs metabolites (iAs + dimethylarsenic acid + monomethylarsonic acid) from human biomonitoring data (both in a range 0.05–0.60 μg kg−1 bw/day for children, adolescents and adults). With data obtained a health risk assessment is performed by existing regulation norms. Several flaws are addressed. For instance, urine DMA used as iAs metabolite is overestimated as its source can also be food items. Further, existing regulation norms (which are under reevaluation by US EPA) are based on a linear dose-response approach valid for high exposure only and highly questionable at low exposure levels. Nevertheless, even by using the conventional approaches with discussed flaws leading to anticipated overestimation, the potential cancer risk was estimated to be of low concern regarding the margins of exposure (MOE) for investigated age groups with average food intake and average iAs concentration in diet (15.3–40.6), supported by MOE calculated from human biomonitoring data (21.4).