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松嫩盆地硝氮驱动的地下水铀富集机理OA

Mechanism of nitrate-driven groundwater uranium enrichment in the Songnen Basin

中文摘要英文摘要

氮素污染导致的地下水重金属次生污染是当前研究的重点和热点.本研究旨在探究地下水中硝氮的分布、来源及其对地下水中铀迁移转化的控制机制.本研究综合采用水化学、NO3-氮氧同位素及水文地球化学模拟的方法,探究了松嫩盆地西部山前倾斜平原地下水中NO3-来源、转化及其驱动的地下水中铀富集过程.研究区地下水沿流向逐渐由氧化环境演变至还原环境,氧化区地下水铀质量浓度(平均14.2 μg/L)显著高于还原区(平均4.1 gg/L);氧化区地下水NO3-平均质量浓度高达188 mg/L,还原区普遍低于10mg/L.NO3-氮氧同位素结果表明:氧化区地下水NC3-主要来自土壤NH4+及NH4+氮肥的硝化作用;而在还原区则主要来自NO3-氮肥的输入.氧化区高浓度的NO3-一方面将固态U(Ⅳ)氧化为溶解态U(Ⅵ),另一方面通过驱动碳酸盐岩风化导致Ca-U-CO3三元络合物的形成,进一步促进了地下水铀的富集;还原区主要发生硅酸盐岩风化及Ca2+与Na+离子交换过程,地下水氧化还原电位和Ca2+浓度均较低,不利于地下水铀的富集.本研究对于理解地下水NO3-污染导致的次生铀浓度超标具有重要的理论意义.

Nitrogen pollution-induced secondary contamination of heavy metals in groundwater is a current focal point and hot topic of research.The study aims to investigate the distribution and sources of NO3-in groundwater,as well as its controlling mechanisms on uranium(U)migration and transformation in groundwater.This study comprehensively employed hydrogeochemical analysis,NO3-nitrogen and oxygen isotopes,and hydrogeochemical modeling to investigate the sources and transformation processes of NO3-,and the relevant driving mechanism on U enrichment in groundwater from the western piedmont plain of the Songnen Basin.The results indicate that the groundwater in the study area gradually evolves from an oxidizing environment to a reducing environment along the groundwater flow path.The average U concentration(14.2 μg/L)in the oxic zone is significantly higher than that in the anoxic zone(4.1 μg/L).The average concentration of NO3-in the groundwater of the oxic zone is as high as 188 mg/L,while it is generally below 10 mg/L in the anoxic zone.The results of NO-nitrogen and oxygen isotopes suggest that NO3-in groundwater from the oxic zone mainly originates from the nitrification of soil NH4+and NH4+fertilizers,while it primarily comes from the input of NO3-fertilizers in the anoxic zone.In the oxic zone,high concentration of NO3-not only oxidizes solid U(Ⅳ)to soluble U(Ⅵ)but also promotes the formation of Ca-U-CO3 ternary complexes through the weathering of carbonate rocks,thereby further promoting the enrichment of U in groundwater.In the anoxic zone,the main processes are the weathering of silicate minerals and the cation exchange between Ca2+and Na+.The groundwater redox potential and Ca2+concentrations are both low in the anoxic zone,which are not conducive to the enrichment of U in groundwater.This study poses considerable theoretical importance for understanding the secondary U contamination in groundwater caused by NO3-pollution.

高志鹏;郭华明;丁正;姜春平;胡学达;徐达

中国地质大学(北京)水利部地下水保护重点实验室(筹),北京 100083||中国地质大学(北京)地质微生物与环境全国重点实验室,北京 100083||中国地质大学(北京)深时数字地球前沿科学中心,北京 100083中国地质大学(北京)水利部地下水保护重点实验室(筹),北京 100083||中国地质大学(北京)地质微生物与环境全国重点实验室,北京 100083||中国地质大学(北京)深时数字地球前沿科学中心,北京 100083中国地质大学(北京)水利部地下水保护重点实验室(筹),北京 100083中国地质大学(北京)水利部地下水保护重点实验室(筹),北京 100083中国地质大学(北京)水利部地下水保护重点实验室(筹),北京 100083中国地质大学(北京)水利部地下水保护重点实验室(筹),北京 100083

天文与地球科学

松嫩盆地地下水硝氮富集机理

Songnen Basingroundwaternitrateuraniumenrichment mechanism

《水文地质工程地质》 2026 (1)

12-22,11

国家自然科学基金项目(4213050942102285)"深时数字地球"中央高校科技领军人才团队项目(2652023001)中央高校基本科研业务费新教师基本科研能力提升项目(2652022040)自然资源部矿业城市自然资源调查监测与保护重点实验室开放课题(2023-B07)

10.16030/j.heg.202503051

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