土壤铁锰结核的环境地球化学行为研究进展

Environmental Geochemical Behavior of Soil Ferromanganese Nodules: Research Progress

  • 摘要: 铁锰结核(FMNs)是成土过程的副产物,在岩溶地质高背景区广泛发育,是解释岩溶区土壤重金属“高总量、低生物有效性”现象的核心。然而,目前仍对其微观机制认识不足,结核动态形成演化及其环境行为的影响缺乏系统关联以及在不同表生环境下,结核地球化学行为的差异性与规律尚未作出清晰总结等问题。本文系统综述了土壤铁锰结核研究的最新进展,包括:①归纳了结核的形成机理、演化过程及其古环境指示意义:不同物理、化学以及生物因素共同控制结核的规律性生长,其中最核心的驱动因素是氧化还原电位。对比不同表生环境下结核的地球化学特征,提出可能的影响路径模式;②总结了结核的生态效应以及对重金属的富集机制研究与实验技术:铁锰结核中Cd、Pb、Ni等元素含量可达对应土壤的数十倍,且pH浸出实验的最大释放量仅为17%(As)。通过扩展X射线吸收精细结构光谱(EXAFS)、X射线吸收近边缘结构光谱(XANES)、激光剥蚀电感耦合等离子体质谱(LA-ICP-MS)等证实,结核通过表面络合、专性吸附及共沉淀等方式强力固定重金属。结核可以通过氧化或吸附影响砷、铬、磷等特征元素迁移转化。未来研究亟需建立基于环境参数的动态风险预警模型,加强多学科交叉融合,将结核的环境效应研究成果纳入土壤环境质量标准和风险管控实践中,实现土地资源的精细化管理和安全利用,为地质高背景区土壤风险精准评价与土地安全利用提供科学依据。

     

    Abstract: Ferromanganese nodules (FMNs) are by-products of soil formation processes, widely developed in karst geological areas with high background, and are the core to explain the phenomenon of “high total content and low bioavailability” of heavy metals in soils in karst regions. However, there is still a lack of understanding of their micro-mechanisms; the lack of systematic correlation between the dynamic formation and evolution of nodules and their environmental behaviors, as well as the unclear summary of the differences and regularities of nodule geochemical behaviors under different epigenetic environments. This article systematically reviews the latest progress in soil ferromanganese nodule research, including: (1) The formation mechanism, evolutionary process, and paleoenvironmental significance of nodules are summarized: Different physical, chemical, and biological factors jointly control the regular growth of nodules, with the most core driving factor being the redox potential. By comparing the geochemical characteristics of nodules under different epigenetic environments, a possible influence path model is proposed; (2) The ecological effects of nodules and the research on the enrichment mechanisms of heavy metals, as well as the experimental techniques, are summarized: The contents of Cd, Pb, Ni, and other elements in ferromanganese nodules can reach dozens of times that of the corresponding soil, and the maximum release amount in pH leaching experiments is only 17% (As). By extending X-ray absorption fine structure spectroscopy (EXAFS), X-ray absorption near edge structure spectroscopy (XANES), laser ablation inductively coupled plasma-mass spectrometry (LA-ICP-MS), and other techniques, it is confirmed that nodules strongly fix heavy metals through surface complexation, specific adsorption, and co-precipitation. Nodules can affect the migration and transformation of characteristic elements such as arsenic, chromium, and phosphorus through oxidation or adsorption. Future research urgently needs to establish a dynamic risk warning model based on environmental parameters, strengthen interdisciplinary integration, incorporate the research results of nodule environmental effects into soil environmental quality standards and risk management practices, achieve refined management and safe utilization of land resources, and provide scientific basis for the precise evaluation of soil risks in geological high background areas and the safe utilization of land.

     

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