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利用玉米和冬小麦从污染农田中化学强化提取风险元素:三年期间的表现和金属迁移。

Chemically enhanced phytoextraction of risk elements from a contaminated agricultural soil using Zea mays and Triticum aestivum: performance and metal mobilization over a three year period.

机构信息

Department of Agro-Environmental Chemistry and Plant Nutrition, Czech University of Life Sciences Prague, Kamýcká, Prague-Suchdol, Czech Republic.

出版信息

Int J Phytoremediation. 2012 Sep;14(8):754-71. doi: 10.1080/15226514.2011.619231.

Abstract

Enhanced phytoextraction using EDTA for the remediation of an agricultural soil contaminated with less mobile risk elements Cd and Pb originating from smelting activities in Príbram (Czech Republic) was assessed on the laboratory and the field scale. EDTA was applied to the first years crop Zea mays. Metal mobilization and metal uptake by the plants in the soil were monitored for two additional years when Triticum aestivum was planted. The application ofEDTA effectively increased water-soluble Cd and Pb concentrations in the soil. These concentrations decreased over time. Anyhow, increased concentrations could be still observed in the third experimental year indicating a low possibility of groundwater pollution after the addition of EDTA during and also after the enhanced phytoextraction process under prevailing climatic conditions. EDTA-applications caused phytotoxicity and thereby decreased biomass production and increased Cd and Pb uptake by the plants. Phytoextraction efficiency and phytoextraction potential were too low for Cd and Pb phytoextraction in the field in a reasonable time frame (as less than one-tenth of a percent of total Cd and Pb could be removed). This strongly indicates that EDTA-enhanced phytoextraction as implemented in this study is not a suitable remediation technique for risk metal contaminated soils.

摘要

采用 EDTA 强化植物提取技术修复源自普里布拉姆(捷克共和国)冶炼活动的农业土壤中较不移动的风险元素 Cd 和 Pb 污染的研究在实验室和田间尺度进行了评估。EDTA 被应用于第一年的作物玉米。当种植冬小麦时,监测了两年中 EDTA 对土壤中金属的迁移和植物的吸收。EDTA 的应用有效地增加了土壤中水溶性 Cd 和 Pb 的浓度。这些浓度随着时间的推移而降低。然而,在第三个实验年仍能观察到增加的浓度,表明在增强的植物提取过程中添加 EDTA 后,在盛行的气候条件下,即使在添加 EDTA 期间和之后,地下水污染的可能性也很低。EDTA 的应用导致植物毒性,从而降低了生物量的产生并增加了植物对 Cd 和 Pb 的吸收。在合理的时间框架内(因为只能去除总 Cd 和 Pb 的不到十分之一),田间的 Cd 和 Pb 植物提取的提取效率和提取潜力都太低,无法进行植物提取。这强烈表明,本研究中实施的 EDTA 强化植物提取技术并不是一种适合修复风险金属污染土壤的修复技术。

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