Ding Hongyu, Zheng Mingxia, Yan Lina, Zhang Xiaoyu, Liu Lu, Sun Yuanyuan, Su Jing, Xi Beidou, Yu Huibin
State Key Laboratory of Environmental Criteria and Risk Assessment, and State Environmental Protection Key Laboratory of Simulation and Control of Groundwater Pollution, Chinese Research Academy of Environmental Sciences, Beijing 100012, China; College of Water Science, Beijing Normal University, Beijing 100875, China.
State Key Laboratory of Environmental Criteria and Risk Assessment, and State Environmental Protection Key Laboratory of Simulation and Control of Groundwater Pollution, Chinese Research Academy of Environmental Sciences, Beijing 100012, China.
Water Res. 2025 Apr 1;273:122978. doi: 10.1016/j.watres.2024.122978. Epub 2024 Dec 20.
Dissolved organic matter (DOM) represents one of the most active elements in aquatic systems, whose fraction is engaged in chemical and biological reactions. However, fluorescence, molecular diversity and variations of DOM in groundwater systems with the alteration of surface water recharge remain unclear. Herein, Excitation-emission matrix (EEM) fluorescence spectroscopy and Fourier transform ion cyclotron resonance mass spectrometry (FT-ICR MS) combined with principal component coefficients, parallel factor analyses (PARAFAC) with two‒dimensional correlation spectroscopy (2D-COS) were applied in this study. EEM data reassembled for principal component analysis (PCA) highlighted differences in tryptophan-like peak between groundwater collected parallel to the river (PR) and those taken vertical to the river (VR). PARAFAC have identified six components, i.e., microbial-related humic substances (C1 and C6), protein-like substances (C2 and C5), and terrestrial humic-like substances (C3 and C4). In the PR direction, variations of fluorescence components were dominated by terrestrial humic-like substances, while microbial humic-like substances predominated in the VR direction, as revealed by 2D-COS analysis. FT-ICR MS data showed a similar DOM molecular evolution trend in groundwater. Specifically, biodegradable molecular formulae decreased with a diminishing contribution of river water to groundwater recharge. This decrease was accompanied by a decrease in OS and OS components, which highlight the influence of anthropogenic river water on groundwater DOM characteristics. Groundwater DOM variations were attributed to the influx of bioavailable and low-oxidized components and the release of terrestrial humic-like substances during river water recharge processes. This study contributes valuable insights into the transformations of DOM in groundwater systems influenced by surface water recharge, enhancing our understanding of the interplay between surface water and groundwater quality.
溶解有机物(DOM)是水生系统中最活跃的元素之一,其部分参与了化学和生物反应。然而,随着地表水补给的变化,地下水系统中DOM的荧光、分子多样性和变化情况仍不清楚。在此,本研究应用了激发-发射矩阵(EEM)荧光光谱法和傅里叶变换离子回旋共振质谱法(FT-ICR MS),并结合主成分系数、平行因子分析(PARAFAC)和二维相关光谱法(2D-COS)。重新组装用于主成分分析(PCA)的EEM数据突出了与河流平行采集的地下水(PR)和与河流垂直采集的地下水(VR)之间类色氨酸峰的差异。PARAFAC识别出六个成分,即微生物相关的腐殖质(C1和C6)、类蛋白质物质(C2和C5)以及陆地类腐殖质(C3和C4)。二维相关光谱分析表明,在PR方向上,荧光成分的变化主要由陆地类腐殖质主导,而在VR方向上,微生物类腐殖质占主导。FT-ICR MS数据显示地下水DOM分子具有相似的演化趋势。具体而言,随着河水对地下水补给贡献的减少,可生物降解的分子式减少。这种减少伴随着氧化态和氧化态成分的减少,这突出了人为河水对地下水DOM特征的影响。地下水DOM的变化归因于河水补给过程中生物可利用和低氧化态成分的流入以及陆地类腐殖质的释放。本研究为受地表水补给影响的地下水系统中DOM的转化提供了有价值的见解,增进了我们对地表水与地下水水质相互作用的理解。