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Biochar as possible long-term soil amendment for phytostabilisation of TE-contaminated soils

机译:生物炭作为长期土壤改良剂,可用于TE污染土壤的植物稳定化

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Soils contaminated by trace elements (TEs) pose a high risk to their surrounding areas as TEs can spread by wind and water erosion or leaching. A possible option to reduce TE transfer from these sites is phytostabilisation. It is a long-term and cost-effective rehabilitation strategy which aims at immobilising TEs within the soil by vegetation cover and amendment application. One possible amendment is biochar. It is charred organic matter which has been shown to immobilise metals due to its high surface area and alkaline pH. Doubts have been expressed about the longevity of this immobilising effect as it could dissipate once the carbonates in the biochar have dissolved. Therefore, in a pot experiment, we determined plant metal uptake by ryegrass (Lolium perenne) from three TE-contaminated soils treated with two biochars, which differed only in their pH (acidic, 2.80; alkaline, 9.33) and carbonate (0.17 and 7.3 %) content. Root biomass was increased by the application of the alkaline biochar due to the decrease in TE toxicity. Zinc and Cu bioavailability and plant uptake were equally reduced by both biochars, showing that surface area plays an important role in metal immobilisation. Biochar could serve as a long-term amendment for TE immobilisation even after its alkalinity effect has dissipated.
机译:微量元素(TEs)污染的土壤对其周围地区构成高风险,因为TEs可能因风和水蚀或淋溶而扩散。减少这些部位TE转移的一种可能选择是植物稳定作用。这是一项长期且具有成本效益的修复策略,旨在通过植被覆盖和施用改良剂将TE固定在土壤中。一种可能的修正是生物炭。它是焦化的有机物,由于其高表面积和碱性pH值,已被证明可以固定金属。人们对这种固定作用的寿命表示怀疑,因为一旦生物炭中的碳酸盐溶解,这种固定作用就会消失。因此,在盆栽实验中,我们确定了黑麦草(黑麦草)从三种用两种生物炭处理过的TE污染土壤中吸收的植物金属,其中两种生物炭的pH值(酸性,2.80;碱性,9.33)和碳酸盐(0.17和7.3)不同%)的内容。由于TE毒性的降低,通过施用碱性生物炭增加了根生物量。两种生物炭均降低了锌和铜的生物利用度和植物吸收量,表明表面积在金属固定化中起着重要作用。即使其碱性效应消失,Biochar仍可作为TE固定化的长期改良剂。

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