Key Laboratory of Groundwater Quality and Health (China University of Geosciences), Ministry of Education, Wuhan 430078, China; State Environmental Protection Key Laboratory of Source Apportionment and Control of Aquatic Pollution, School of Environmental Studies, Wuhan 430078, China.
Key Laboratory of Groundwater Quality and Health (China University of Geosciences), Ministry of Education, Wuhan 430078, China; State Environmental Protection Key Laboratory of Source Apportionment and Control of Aquatic Pollution, School of Environmental Studies, Wuhan 430078, China.
Water Res. 2024 Oct 15;264:122215. doi: 10.1016/j.watres.2024.122215. Epub 2024 Aug 6.
The excessive presence of geogenic ammonium (NH) in groundwater poses a global environmental concern, commonly linked to the degradation of nitrogen-containing dissolved organic matter (DOM). However, there is a gap in systematic studies on the combination of soluble organic matter (SOM) in sediments and DOM in groundwater, with few indoor incubation experiments to validate their degradation pathways. This study utilized ultrahigh-resolution Fourier transform ion cyclotron resonance mass spectrometry to analyze the molecular characteristics of DOM and SOM in aquifer systems affected by geogenic NH. Subsequently, indoor incubation experiments spanning up to 140 d were conducted to verify the degradation pathways. The experimental results revealed a two-phase degradation process for both the DOM and SOM. The initial stage was characterized by the degradation of aliphatic compounds (ALC) with the production of polyphenols (PPE) and highly unsaturated compounds (HUC). The second stage was dominated by the degradation of PPE and HUC, accompanied by the re-consumption of some ALC, while more recalcitrant HUC persisted. Notably, the first stage of SOM degradation exceeded that of DOM degradation, indicating that SOM exhibited greater resistance to aging. This phenomenon may be attributed to a wider range of active enzymes in sediments, the rapid replenishment of SOM by organic matter in sediments, or the accelerated degradation of DOM. The experimental results aligned with the molecular characterization of DOM and SOM in actual aquifer systems. It is hypothesized that NH produced through the direct mineralization of SOM may contribute more to the enrichment of NH in groundwater than that produced through the mineralization of DOM. This study is the first to analyze DOM and SOM together in aquifer systems and validate their degradation pathways through incubation experiments, thereby providing novel insights into the enrichment of geogenic NH in groundwater.
地下水中超量存在的地球成因铵(NH)引起了全球环境关注,通常与含氮溶解有机质(DOM)的降解有关。然而,对于沉积物中可溶性有机质(SOM)与地下水 DOM 的结合,系统研究仍存在空白,室内孵育实验也很少验证其降解途径。本研究利用超高分辨傅里叶变换离子回旋共振质谱分析了受地球成因 NH 影响的含水层系统中 DOM 和 SOM 的分子特征。随后,进行了长达 140 天的室内孵育实验,以验证降解途径。实验结果表明,DOM 和 SOM 均经历了两阶段降解过程。初始阶段以脂肪族化合物(ALC)的降解为特征,生成多酚(PPE)和高度不饱和化合物(HUC)。第二阶段则以 PPE 和 HUC 的降解为主,同时部分 ALC 被重新消耗,而更难降解的 HUC 则持续存在。值得注意的是,SOM 的初始降解阶段超过了 DOM 的降解阶段,表明 SOM 对老化具有更大的抵抗力。这种现象可能归因于沉积物中具有更广泛活性的酶、沉积物中有机质的快速补充,或者 DOM 的加速降解。实验结果与实际含水层系统中 DOM 和 SOM 的分子特征相吻合。据推测,通过 SOM 的直接矿化产生的 NH 可能比通过 DOM 矿化产生的 NH 对地下水 NH 的富集贡献更大。本研究首次在含水层系统中同时分析 DOM 和 SOM,并通过孵育实验验证其降解途径,为地下水地球成因 NH 的富集提供了新的见解。