Univ. Nîmes, EA 7352 CHROME, rue du Dr Georges Salan, 30021 Nîmes, France.
Univ. Nîmes, EA 7352 CHROME, rue du Dr Georges Salan, 30021 Nîmes, France.
Sci Total Environ. 2019 Feb 15;651(Pt 1):1126-1136. doi: 10.1016/j.scitotenv.2018.09.222. Epub 2018 Sep 20.
The transfer of metal and metalloid trace elements (MTEs) from contaminated soil to grapevines is a major issue for grape consumption and for the associated health risks. Based on an isotopic approach, we shed light on the concept of MTE bioavailability. The bioavailable fractions are identified by using the Sr-isotope ratio as a proxy for MTEs. This allows us to differentiate three soil reservoirs: the 'current available fraction' in soil water, the 'reserve available fraction' stored in mineral phases of the soil fractions, and the 'non-available fraction'. The reserve available fraction, representing 10 to 60% of bulk soil depending on the MTE, includes the exchangeable, carbonates, humic substance and oxides fractions. The Sr/Sr isotopic signatures of grape berries and vine leaves show an additional source of MTEs, which is imported by foliar uptake and can contribute up to 10% of the MTEs in leaves. In addition, root-uptake and translocation rates show high accumulation rates of Co, Sn and Cu, and low ones for As, Sb, Zn and Cd. A daily intake between 1 and 3 kg of (dry grapes) would reach the benchmark dose level for a 0.5% (BMDL). While such a daily intake of grapes is unreasonable, consumption of other local vegetables and fruit would contribute to the daily intake. Hence, a chronic arsenic exposure is of great concern for human health in mining areas. We outline the importance of geochemical tracers, such as Sr isotopes, when determining the transfer and translocation of MTEs in plants. Our method presents a high-precision evaluation of the bioavailability and bioaccumulation of MTEs, and a better understanding of these processes in plants, thus leading to a better assessment of the environmental risk on human health.
金属和类金属微量元素(MTEs)从污染土壤向葡萄藤的转移是葡萄消费及其相关健康风险的一个主要问题。基于同位素方法,我们揭示了 MTE 生物利用度的概念。通过 Sr 同位素比作为 MTE 的替代物,确定了生物可利用的分数。这使我们能够区分三种土壤储层:土壤水中的“当前可用分数”、土壤矿物相储存的“储备可用分数”以及“不可用分数”。储备可用分数代表了 bulk soil 的 10%至 60%,具体取决于 MTE,包括可交换态、碳酸盐、腐殖质和氧化物分数。葡萄浆果和葡萄藤叶片的 Sr/Sr 同位素特征显示了 MTE 的另一个来源,这些 MTE 是通过叶片吸收而进入的,可贡献叶片中 MTE 的 10%。此外,根吸收和转运速率显示 Co、Sn 和 Cu 的积累率较高,而 As、Sb、Zn 和 Cd 的积累率较低。每天摄入 1 至 3 公斤(干葡萄)将达到 0.5%(BMDL)的基准剂量水平。虽然每天摄入这么多葡萄是不合理的,但食用其他当地蔬菜和水果也会导致每日摄入量增加。因此,矿区的慢性砷暴露对人类健康构成了极大的威胁。我们概述了地球化学示踪剂(如 Sr 同位素)在确定 MTE 在植物中的迁移和转运中的重要性。我们的方法对 MTE 的生物利用度和生物积累进行了高精度评估,并更好地了解了这些植物中的过程,从而更好地评估了对人类健康的环境风险。