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

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 fractionation and isotope composition 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 (Δ 114/110 Cd C6-C1 = −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. • Similar decrease in Cd concentration in soil aggregate of different size fractions. • Similar mechanism in Cd uptake from soil aggregate of different size fractions. • Zn exchange among soil aggregate of different size fractions during phytoextraction. • Negligible Zn isotope fractionation was found in aggregate of different size fractions.

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Publication Details

Journal
Soil & Environmental Health
Published
2025-01-01
DOI
https://doi.org/10.1016/j.seh.2025.100129
Citations
3
Primary Topic
Heavy metals in environment
Type
article
Field-Weighted Citation Impact
1.51

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article

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

Jia‐wen Zhou, Ting Gao, Peter Christie, Barry J. Coles et al.
3 citations
Soil & Environmental Health
Heavy metals in environment
1.51
article

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

Jia‐wen Zhou, Ting Gao, Peter Christie, Barry J. Coles, Jingqi Dong, Longhua Wu, Rebekah E. T. Moore, Mark Rehkämper, Katharina Kreissig
article en
3 citations

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 fractionation and isotope composition 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 (Δ 114/110 Cd C6-C1 = −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. • Similar decrease in Cd concentration in soil aggregate of different size fractions. • Similar mechanism in Cd uptake from soil aggregate of different size fractions. • Zn exchange among soil aggregate of different size fractions during phytoextraction. • Negligible Zn isotope fractionation was found in aggregate of different size fractions.

Soil & Environmental HealthVol. 3(1)
Chinese Academy of Sciences (CN), Chinese Academy for Environmental Planning (CN), Institute of Soil Science (CN), Imperial College London (GB)
Science and Technology Facilities Council
Zero hunger
Openalex Percentile: Top 22%
Heavy metals in environment
1.51
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