Li Qi, Wang Yanhong, Li Yichun, Li Linfeng, Tang Mingdeng, Hu Weifang, Chen Li, Ai Shaoying
Institute of Agricultural Resources and Environment, Guangdong Academy of Agricultural Sciences, Guangzhou 510640, China; Key Laboratory of Plant Nutrition and Fertilizer in South Region, Ministry of Agriculture, Guangzhou 510640, China; Guangdong Key Laboratory of Nutrient Cycling and Farmland Conservation, Guangzhou 510640, China.
College of Natural Resources and Environment, Northwest A&F University, Yangling 712100, China.
Sci Total Environ. 2022 Jun 15;825:153862. doi: 10.1016/j.scitotenv.2022.153862. Epub 2022 Feb 15.
Heavy metal (HM) pollution of soils is a globally important ecological and environmental problem. Previous studies have focused on i) tracking pollution sources in HM-contaminated soils, ii) exploring the adsorption capacity and distribution of HMs, and iii) assessing phyto-uptake of HMs and their ecotoxicity. However, few reviews have systematically summarized HM pollution in soil-plant systems over the past decade. Understanding the mechanisms of interaction between HMs and solid soil components is consequently key to effectively controlling and remediating HM pollution. However, the compositions of solid soil phases are diverse, their structures are complex, and their spatial arrangements are heterogeneous, all leading to the formation of soil micro-domains that exhibit different particle sizes and surface properties. The various soil components and their interactions ultimately control the speciation, transformation, and bioavailability of HMs in soils. Over the past few decades, the extensive application of advanced instrumental techniques and methods has greatly expanded our understanding of the behavior of HMs in organic mineral assemblages. In this review, studies investigating the immobilization of HMs by minerals, organic compounds, microorganisms, and their associated complexes are summarized, with a particular emphasis on the interfacial adsorption and immobilization of HMs. In addition, methods for analyzing the speciation and distribution of HMs in aggregates of natural soils with different particle sizes are also discussed. Moreover, we also review the methods for speciating HMs at mineral-organic micro-scale interfaces. Lastly, developmental prospects for HM research at inorganic-organic interfaces are outlined. In future research, the most advanced methods should be used to characterize the interfaces and in situ characteristics of metals and metal complexes. In particular, the roles and contributions of microorganisms in the immobilization of HMs at complex mineral-organic interfaces require significant further investigation.
土壤重金属(HM)污染是一个全球性的重要生态和环境问题。以往的研究主要集中在:i)追踪重金属污染土壤的污染源;ii)探索重金属的吸附容量和分布;iii)评估重金属的植物吸收及其生态毒性。然而,很少有综述系统地总结过去十年土壤 - 植物系统中的重金属污染情况。因此,了解重金属与土壤固体成分之间的相互作用机制是有效控制和修复重金属污染的关键。然而,土壤固相成分多样,结构复杂,空间排列不均一,所有这些都导致形成了具有不同粒径和表面性质的土壤微域。各种土壤成分及其相互作用最终控制着土壤中重金属的形态、转化和生物有效性。在过去几十年中,先进仪器技术和方法的广泛应用极大地扩展了我们对重金属在有机矿物组合中行为的理解。在本综述中,总结了研究矿物、有机化合物、微生物及其相关络合物对重金属固定作用的研究,特别强调了重金属的界面吸附和固定作用。此外,还讨论了分析不同粒径天然土壤团聚体中重金属形态和分布的方法。此外,我们还综述了在矿物 - 有机微观尺度界面上对重金属进行形态分析的方法。最后,概述了无机 - 有机界面重金属研究的发展前景。在未来的研究中,应使用最先进的方法来表征金属和金属络合物的界面及原位特征。特别是,微生物在复杂矿物 - 有机界面上对重金属固定作用中的作用和贡献需要进一步深入研究。