Molecule-based quantification of dissolved organic matter sources in high-arsenic groundwater

被引:5
|
作者
Qiao, Wen [1 ,2 ]
Gao, Zhipeng [2 ,3 ,4 ]
He, Chen [5 ]
Shi, Quan [5 ]
Han, Shuangbao [6 ,7 ]
Guo, Huaming [2 ,3 ,4 ,6 ,7 ]
机构
[1] China Geol Survey, Minist Nat Resources, China Inst Geoenvironm Monitoring, Key Lab Mine Ecol Effects & Systemat Restorat, Beijing 100081, Peoples R China
[2] China Univ Geosci Beijing, State Key Lab Biogeol & Environm Geol, Beijing 100083, Peoples R China
[3] China Univ Geosci Beijing, Key Lab Groundwater Conservat MWR, Beijing 100083, Peoples R China
[4] China Univ Geosci Beijing, Sch Water Resources & Environm, Beijing 100083, Peoples R China
[5] China Univ Petr, State Key Lab Heavy Oil Proc, Beijing 102249, Peoples R China
[6] China Geol Survey, Ctr Hydrogeol & Environm Geol, Baoding 071051, Peoples R China
[7] China Univ Geosci Beijing, Sch Water Resources & Environm, Beijing 100083, Peoples R China
基金
中国国家自然科学基金;
关键词
Arsenic; FT-ICR MS; Groundwater DOM sources; Relative contribution; WSOM; WESTERN HETAO BASIN; BIOGEOCHEMICAL PROCESSES; CONTAMINATED AQUIFER; RIVER FLOODPLAIN; INNER-MONGOLIA; CARBON; WATER; RELEASE; MASS; CHINA;
D O I
10.1016/j.jhydrol.2023.130352
中图分类号
TU [建筑科学];
学科分类号
0813 ;
摘要
Compositions of dissolved organic matter (DOM) in high-arsenic groundwater are usually sourced from the recharged groundwater DOM and the in-situ mobilized organic matter (OM) from aquifer sediments. However, relative importance of the two sources in DOM remains unclear. To quantify sources of DOM, Fourier transform ion cyclotron resonance mass spectrometry was used to analyze molecular characteristics of groundwater DOM and water-soluble organic matter (WSOM) in sediments along an inferred groundwater flow path in the Hetao Basin, China. Results showed that dissolved arsenic concentrations gradually increased from 1.92 to 402 mu g/L along the flow path, being mainly due to the DOM degradation-triggered Fe(III) oxide reduction. The DOM molecules being unique to the background groundwater represented the in-situ mobilized OM, which showed the similar abundance to the DOM molecules being common to its depth-matched WSOM. An increasing trend of the relative abundance of the in-situ mobilized OM to the total DOM molecules along the flow path was recognized (from 0 % to 44.5 %). This suggests that the relative contribution of the in-situ mobilized OM to the groundwater DOM increased along with dissolved arsenic concentration. Furthermore, the biodegradable pool among the in situ mobilized OM was significantly positively correlated with dissolved arsenic, indicating that this in-situ mobilized OM exhibited a dominant role in groundwater arsenic enrichment. The study provides novel insights into contribution of the in-situ mobilized OM to DOM and arsenic mobility in groundwater systems.
引用
收藏
页数:10
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