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三峡水库消落带土壤中溶解有机物的光谱和分子组成对活性镉迁移的影响

Influence of spectral and molecular composition of dissolved organic matter on labile Cd mobility in riparian soils in the Three Gorges Reservoir, China.

作者信息

Cui Meng, Xu Dongyu, Liu Xiaobo, Lai Xianqiang, Zhang Moli, Gao Bo

机构信息

State Key Laboratory of Simulation and Regulation of Water Cycle in River Basin, China Institute of Water Resources and Hydropower Research, Beijing 100038, China; Department of Water Ecology and Environment, China Institute of Water Resources and Hydropower Research, Beijing 100038, China.

State Key Laboratory of Simulation and Regulation of Water Cycle in River Basin, China Institute of Water Resources and Hydropower Research, Beijing 100038, China; Department of Water Ecology and Environment, China Institute of Water Resources and Hydropower Research, Beijing 100038, China.

出版信息

Sci Total Environ. 2024 Dec 10;955:176736. doi: 10.1016/j.scitotenv.2024.176736. Epub 2024 Oct 8.

Abstract

The periodic anti-seasonal inundation of the Three Gorges Reservoir (TGR) leads to changes in the molecular composition of dissolved organic matter (DOM) in riparian soils, further impacting the geochemical processes and ecological risk of heavy metals. However, the intrinsic driving mechanisms of DOM influencing the cadmium (Cd), a major pollutant in riparian soils in TGR, at the molecular level remain unclear. In this study, the DOM molecular composition, labile Cd in riparian soils and the key driving mechanism before and after flooding were explored using Fourier transform ion cyclotron resonance mass spectrometry (FT-ICR MS), the diffusive gradients in thin films (DGT) and partial least squares path modeling (PLS-PM). A spectral analysis revealed that after flooding, the relative abundance of terrestrial humic-like substances decreased whereas that of microbial humic-like substances increased. Furthermore, FT-ICR MS analysis revealed that the relative abundance of lignin, the main molecular components of DOM in riparian soils, increased after flooding. The linkage of DOM with the concentration and kinetic processes of labile Cd indicated that the higher aromaticity and unsaturation, larger molecular weight, and higher humification level of DOM promoted the mobility of labile Cd from the soil solid phase to the liquid phase. In particular, our findings indicated that at the molecular level, the most significant factor influencing the mobility of labile Cd was lignin, which was primarily governed by the complexation of lignin with labile Cd. The complexation mechanism between lignin and labile Cd resulted in increased ecotoxicological risk of labile Cd after flooding, while the overall ecotoxicological risk was low in riparian soils in TGR. This study provides better insight into the geochemical cycling and fate of toxic elements in reservoir ecosystems under the change of hydrological regime.

摘要

三峡水库(TGR)周期性的反季节蓄水导致河岸土壤中溶解有机物(DOM)的分子组成发生变化,进而影响重金属的地球化学过程和生态风险。然而,DOM在分子水平上影响TGR河岸土壤中主要污染物镉(Cd)的内在驱动机制仍不清楚。在本研究中,利用傅里叶变换离子回旋共振质谱(FT-ICR MS)、薄膜扩散梯度技术(DGT)和偏最小二乘路径模型(PLS-PM),探究了淹水前后DOM的分子组成、河岸土壤中活性Cd以及关键驱动机制。光谱分析表明,淹水后陆地类腐殖质的相对丰度降低,而微生物类腐殖质的相对丰度增加。此外,FT-ICR MS分析表明,河岸土壤中DOM的主要分子成分木质素的相对丰度在淹水后增加。DOM与活性Cd的浓度和动力学过程之间的联系表明,DOM较高的芳香性和不饱和度、较大的分子量以及较高的腐殖化程度促进了活性Cd从土壤固相到液相的迁移。特别是,我们的研究结果表明,在分子水平上,影响活性Cd迁移的最显著因素是木质素,这主要是由木质素与活性Cd的络合作用决定的。木质素与活性Cd之间的络合机制导致淹水后活性Cd的生态毒理学风险增加,而TGR河岸土壤中的总体生态毒理学风险较低。本研究为水文情势变化下水库生态系统中有毒元素的地球化学循环和归宿提供了更好的见解。

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