Kong Jing, Guo Qingjun, Wei Rongfei, Sha Ou, Mao Mingyan, Yang Suchang
School of Environmental and Chemical Engineering, Jiangsu Ocean University, Jiangsu Province, Lianyungang 222000, China; Center for Environmental Remediation, Institute of Geographic Sciences and Natural Resources Research, Chinese Academy of Sciences, Beijing 100101, China.
Center for Environmental Remediation, Institute of Geographic Sciences and Natural Resources Research, Chinese Academy of Sciences, Beijing 100101, China; College of Resources and Environment, University of Chinese Academy of Sciences, Beijing 100049, China.
J Hazard Mater. 2025 Aug 15;494:138394. doi: 10.1016/j.jhazmat.2025.138394. Epub 2025 Apr 23.
Isotopic tracing has been widely used to identify the sources and migration processes of Zn in diverse environments. However, Zn isotope fractionation during the migration process within the mining area poses challenges to the accuracy of isotopic tracing. To address this issue, a representative Pb-Zn mining area in the karst region of southwestern China was selected as the study area, given its long-term tailings' pollution history and the extensive spatial distribution of Zn migration. End-member samples and environmental media (soil, plants, river water and groundwater) were systematically collected, and heavy metal concentrations and isotopic signatures were analyzed. The migration pathways of Zn and associated isotopic fractionation from end members to surrounding environments were comprehensively investigated. Results indicated that tailings constitute the dominant source of Zn, with ZnS weathering being the primary driver of Zn isotopic variability in soils. Eluviation process, characterized by selective transport of soluble Zn enriched in heavy isotopes, was identified as the key mechanism governing Zn migration across the soil-plant-river continuum. Retention processes (adsorption by organic matter, plant uptake, and mineral interactions) exhibited minimal influence on soil Zn isotopic composition. These findings advance the understanding of Zn and Zn isotope cycling in karst ecosystems and provide a scientific basis for formulating pollution control strategies in mining areas.
同位素示踪已被广泛用于识别不同环境中锌的来源和迁移过程。然而,矿区内迁移过程中的锌同位素分馏对同位素示踪的准确性提出了挑战。为解决这一问题,选择了中国西南部喀斯特地区一个具有代表性的铅锌矿区作为研究区域,该矿区有长期的尾矿污染历史以及锌迁移的广泛空间分布。系统采集了端元样品和环境介质(土壤、植物、河水和地下水),并分析了重金属浓度和同位素特征。全面研究了锌从端元到周围环境的迁移途径以及相关的同位素分馏。结果表明,尾矿是锌的主要来源,硫化锌风化是土壤中锌同位素变化的主要驱动因素。以选择性运输富含重同位素的可溶性锌为特征的淋溶过程被确定为控制锌在土壤 - 植物 - 河流连续体中迁移的关键机制。保留过程(通过有机物吸附、植物吸收和矿物相互作用)对土壤锌同位素组成的影响最小。这些发现增进了对喀斯特生态系统中锌和锌同位素循环的理解,并为制定矿区污染控制策略提供了科学依据。