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加拿大一枝黄花中砷形态的吸收和转运。

Arsenic species uptake and translocation in Elodea canadensis.

机构信息

a Facultad Regional Trenque Lauquen , Universidad Tecnológica Nacional , Buenos Aires , Argentina.

b Instituto de Química de San Luis, INQUISAL, Centro Científico-Tecnológico de San Luis (CCT-San Luis), Consejo Nacional de Investigaciones Científicas , Universidad Nacional de San Luis , Ciudad de San Luis , Argentina.

出版信息

Int J Phytoremediation. 2019;21(7):693-698. doi: 10.1080/15226514.2018.1556588. Epub 2019 Jan 18.

Abstract

The capacity of Elodea canadensis to phytofiltrate arsenic species from water was evaluated. Plants were adapted to tap water and supplemented with 15 and 250 µg L of As. Inorganic arsenic species (As III, As V), and organic arsenic compounds: monomethylarsonate (MMA) and dimethylarsinate (DMA) were analyzed. Sampling was carried out at different times after exposure in culture water and plant organs. Plants exposed to 15 µg L of As concentration showed no significant difference on As concentration (95% confidence level) in their organs compared to controls. When plants were exposed to 250 µg L of As concentration, a significant increase of As concentration in plant organs was observed. After 1 h exposure, plants reduce 63.16% the As concentration in the culture water, with a bioaccumulation factor (BF) of 4.3. Under these conditions, E. canadensis accumulate As V in roots and do not translocate it to stems (transfer factor <1). MMA was determined in stems and leaves. E. canadensis effectively phytofiltrate As from tap water of a city located in an arsenic endemic area from concentrations of 36 µg L to undetectable levels (10 ng L).

摘要

研究了加拿大眼子菜对水中砷形态的植物过滤能力。将植物适应于自来水,并补充 15 和 250 μg/L 的砷。分析了无机砷形态(As III、As V)和有机砷化合物:一甲基砷酸盐(MMA)和二甲基砷酸盐(DMA)。在暴露于培养液和植物器官后的不同时间进行采样。与对照相比,暴露于 15 μg/L 砷浓度的植物在器官中的砷浓度(置信水平为 95%)没有显著差异。当植物暴露于 250 μg/L 的砷浓度时,观察到植物器官中的砷浓度显著增加。暴露 1 小时后,植物将培养液中的砷浓度降低了 63.16%,生物积累因子(BF)为 4.3。在这些条件下,E. canadensis 在根中积累 As V,而不将其转运到茎中(转运因子 <1)。在茎和叶中测定了 MMA。E. canadensis 有效地从砷流行地区的城市自来水中过滤砷,将浓度从 36 μg/L 降低到无法检测的水平(10 ng/L)。

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