Department of Agroenvironmental Chemistry and Plant Nutrition, Faculty of Agrobiology, Food and Natural Resources, Czech University of Life Sciences Prague, 165 00, Prague, Czech Republic.
Environ Sci Pollut Res Int. 2017 Aug;24(23):19201-19210. doi: 10.1007/s11356-017-9510-7. Epub 2017 Jun 29.
Willows (Salix spp.) are considered to be effective for the phytoremediation of trace elements from contaminated soils, but their efficiency is limited in heavily polluted soils because of poor growth. Liming can be a desirable measure to decrease the plant availability of elements, resulting in improved plant development. Notably, large root area and maximum soil penetration are basic parameters that improve the efficiency of phytoremediation. The impact of soil chemical properties on willow root anatomy and the distribution of trace elements below-ground have rarely been studied. The effect of liming on root parameters, biomass allocation and trace element distribution in non-harvestable (coarse roots, fine roots, stumps) and harvestable plant parts (twigs and leaves) of Salix × smithiana was assessed at the end of a 4-year pot experiment with two trace element-polluted soils that differed in terms of soil pH. Stump biomass predominated in weakly acidic soil. In neutral soil, the majority of biomass was located in fine roots and stumps; the difference from other plant parts was minor. Trace elements were the most concentrated in fine roots. Translocation to above-ground biomass increased as follows: Pb < As < Zn~Cd. In contrast to Cd and Zn, great differences in As and Pb mobility in plants were recorded after measurements of individual below-ground biomass (stumps < coarse roots < fine roots). Lime application decreased the concentrations of mobile Cd and Zn and related levels in plants, improved biomass production and root parameters and increased the removal of all trace elements in weakly acidic soil. None or minimum differences in the monitored parameters were recorded for dolomite treatments in both soils. The dose and source of liming had crucial effects on root anatomy. Growing willows in limed trace element-polluted soils is a suitable measure for combination of two remediation strategies, i.e. phytoextraction of Cd and Zn and assisted phytostabilization of As and Pb.
柳树(Salix spp.)被认为是有效修复受污染土壤中微量元素的植物,但由于生长不良,它们在污染严重的土壤中的效率有限。石灰处理可以降低元素的植物可利用性,从而改善植物的生长发育。值得注意的是,较大的根面积和最大的土壤穿透深度是提高植物修复效率的基本参数。土壤化学性质对柳树根系解剖结构和地下微量元素分布的影响很少被研究。本研究在为期 4 年的盆栽试验中,研究了石灰处理对受污染土壤中两种不同 pH 值土壤中柳属杂交种(Salix × smithiana)非收获(粗根、细根、树桩)和可收获(嫩枝和叶片)植物部分的根参数、生物量分配和微量元素分布的影响。在弱酸性土壤中,树桩生物量占主导地位。在中性土壤中,大部分生物量位于细根和树桩中;与其他植物部分的差异较小。微量元素在细根中浓度最高。向地上生物量的转运量如下:Pb<As<Zn~Cd。与 Cd 和 Zn 不同,在测量单个地下生物量(树桩<粗根<细根)后,记录到植物中 As 和 Pb 迁移性的差异很大。石灰处理降低了可移动 Cd 和 Zn 的浓度及其在植物中的含量,提高了生物量生产和根参数,并增加了弱酸性土壤中所有微量元素的去除。在两种土壤中,施用白云石对监测参数没有或最小差异。石灰处理的剂量和来源对根解剖结构有重要影响。在石灰处理的受污染土壤中种植柳树是结合两种修复策略的合适措施,即 Cd 和 Zn 的植物提取和 As 和 Pb 的辅助稳定化。