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DOM 影响 Hg 污染梯度下稻田土壤中的 Hg 甲基化。

DOM influences Hg methylation in paddy soils across a Hg contamination gradient.

机构信息

State Key Laboratory of Environmental Geochemistry, Institute of Geochemistry, Chinese Academy of Sciences, Guiyang, 550081, China; University of Chinese Academy of Sciences, Beijing, 100049, China; Geology Department, Faculty of Science, Al-Azhar University, Assiut, 71524, Egypt.

State Key Laboratory of Environmental Geochemistry, Institute of Geochemistry, Chinese Academy of Sciences, Guiyang, 550081, China.

出版信息

Environ Pollut. 2023 Apr 1;322:121237. doi: 10.1016/j.envpol.2023.121237. Epub 2023 Feb 7.

Abstract

Rice paddies provide optimum conditions for Hg methylation, and paddy soil is a hot spot for Hg methylation and the predominant source of methylmercury (MeHg) accumulated in rice grains. The role of dissolved organic matter (DOM) in controlling Hg bioavailability and methylation in rice paddy systems remains unclear. Paddy soils from eight various cultivation sites in China were chosen to investigate the variations in soil DOM and the influence of DOM concentration and optical characteristics on Hg methylation in rice paddy systems. In the present study, 151 rhizosphere soil samples were collected, and UV-Vis absorption and fluorescent spectroscopy were used to identify the optical properties of DOM. The relationship between MeHg and DOM's optical property indices revealed the production of MeHg consumes lower molecular weight DOM. Moreover, the correlation between DOM concentration and its optical characteristics highlighted the significant role of humic components on MeHg variability in paddy soil. Variation and correlation results demonstrated the allochthonous origin of DOM in the Hg-contaminated soil, with a higher molecular weight and humic character of DOM, as well as the dominant role of autochthonous DOM in promoting Hg methylation in uncontaminated soil. The current study indicated that soil organic matter and its dissolved fractions tend to limit Hg bioavailability and subsequently diminish MeHg production in contaminated paddy soils. Furthermore, the leading roles of allochthonous DOM in protecting MeHg from degradation and autochthonous DOM signatures in enhancing MeHg production in paddy soils. Overall, these findings provide insight into the correlative distributions of DOM and Hg along a Hg concentration gradient in paddy soil, thereby highlighting their potential role in controlling Hg bioavailability and regulating Hg methylation in the soil ecosystems.

摘要

稻田为汞的甲基化提供了最佳条件,而稻田土壤是汞甲基化的热点,也是水稻籽粒中积累的甲基汞(MeHg)的主要来源。溶解有机质(DOM)在控制水稻田系统中汞生物利用度和甲基化方面的作用仍不清楚。本研究选择了中国 8 个不同种植地点的稻田土壤,以研究土壤 DOM 的变化以及 DOM 浓度和光学特性对水稻田系统中汞甲基化的影响。本研究共采集了 151 个根际土壤样品,利用紫外-可见吸收和荧光光谱法来鉴定 DOM 的光学特性。MeHg 与 DOM 光学特性指数之间的关系表明,MeHg 的生成消耗了低分子量的 DOM。此外,DOM 浓度与其光学特性之间的相关性突出了腐殖质成分在稻田土壤中对 MeHg 变异性的重要作用。变异和相关性结果表明,受污染土壤中 DOM 具有异源来源,其分子量较高,具有腐殖质特征,而未受污染土壤中 DOM 具有促进 Hg 甲基化的自源特征。本研究表明,土壤有机质及其溶解组分倾向于限制汞的生物利用度,从而减少污染稻田中 MeHg 的生成。此外,外来 DOM 在外源 DOM 保护 MeHg 免受降解方面起着主导作用,而自源 DOM 特征则在增强 MeHg 的生成方面起着主导作用。总的来说,这些发现深入了解了 DOM 和 Hg 在稻田土壤中沿 Hg 浓度梯度的相关分布,从而突出了它们在控制土壤生态系统中 Hg 生物利用度和调节 Hg 甲基化方面的潜在作用。

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