Zinc and cadmium release from soil aggregate of different size fractions during repeated phytoextraction with Sedum plumbizincicola: Insight from stable isotope analysis

Jiawen Zhou , Jingqi Dong , Rebekah E.T. Moore , Mark Rehkämper , Katharina Kreissig , Barry Coles , Ting Gao , Peter Christie , Longhua Wu
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Abstract

Studies based on metal isotope changes at micro-scale interfaces within soils (i.e., between aggregates of different size fractions) can provide further insight into soil-plant interactions during long-term phytoextraction. Here, aggregate size separation was conducted on two contaminated soils that underwent phytoextraction using Zn/Cd hyperaccumulator Sedum plumbizincicola over six consecutive seasons. The dynamic changes in Zn and Cd concentrations, chemical fractionations and isotope compositions in soil aggregates were investigated. As phytoextraction proceeded from the first (C1) to the sixth (C6) season, shoot Zn displayed a marginally heavier isotope composition despite the essentially constant Zn isotope composition of bulk soils and the 50–250, 5–50, 1–5, and <1 ​μm aggregate size fractions. Most likely, this results from moderate depletion of Zn in the bulk soils (by ​≤ ​21%) and gradual release of heavy Zn isotopes into soil bioavailable pool due to soil acidification and Zn exchange during repeated phytoextraction. Light isotopes of Cd were significantly enriched in all aggregates of different size fractions (Δ114/110CdC6C1 ​= ​−0.14 ​± ​0.04 to −0.02 ​± ​0.04‰) with similar decreases in Cd concentrations (50–64% and 87–92% in two soils) over the five consecutive seasons. Rayleigh modelling produced similar Cd isotope fractionation factors for aggregates of different size fractions, indicating that similar mechanisms controlled Cd release from soil aggregates. In contrast to other plants preferring light Cd isotopes, Zn/Cd hyperaccumulator continuously took up heavier Cd isotopes from soils. The results were due to the enhanced root exudation to mobilize more Cd from soil solids and organic ligands excreted from roots preferentially complexed heavy Cd isotopes based on density functional theory. The different isotopic behaviours of Zn and Cd suggest different processes controlling their migration in the soil-plant system.

Abstract Image

不同粒径土壤团聚体中锌和镉的释放:来自稳定同位素分析的启示
基于土壤内微尺度界面(即不同大小组分团聚体之间)金属同位素变化的研究可以进一步了解长期植物提取过程中土壤-植物的相互作用。采用Zn/Cd超富集植物Sedum plumbizincicola对两种污染土壤进行了连续6个季节的团聚体粒度分离。研究了土壤团聚体中Zn、Cd浓度、化学分异和同位素组成的动态变化。从第1季(C1)到第6季(C6),尽管总体土壤和50-250、5-50、1 - 5和1 μm团聚体组分的Zn同位素组成基本保持不变,但茎部Zn同位素组成偏重。这很可能是由于在重复植物提取过程中,由于土壤酸化和锌交换,土壤中锌的适度损耗(≤21%)和重锌同位素逐渐释放到土壤生物可利用库中造成的。Cd轻同位素在不同粒径团聚体中均显著富集(Δ114/110CdC6-C1 = - 0.14±0.04 ~ - 0.02±0.04‰),且连续5个季节Cd浓度下降幅度相似(分别为50 ~ 64%和87 ~ 92%)。Rayleigh模型得出不同粒径团聚体的Cd同位素分异因子相似,表明控制土壤团聚体Cd释放的机制相似。相对于其他植物对轻Cd同位素的偏好,Zn/Cd超积累体不断从土壤中吸收较重的Cd同位素。根据密度泛函数理论,这是由于根系分泌物增加,从土壤固体中动员了更多的Cd,根系分泌的有机配体优先络合重Cd同位素。锌和镉在土壤-植物系统中不同的同位素行为表明控制其迁移的不同过程。
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