College of Environmental Science & Engineering, Yancheng Institute of Technology, Yancheng, Jiangsu Province 224051, China; Key Laboratory of Environmental Biotechnology, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, China.
College of Environmental Science & Engineering, Yancheng Institute of Technology, Yancheng, Jiangsu Province 224051, China.
Sci Total Environ. 2021 May 20;770:144791. doi: 10.1016/j.scitotenv.2020.144791. Epub 2021 Jan 23.
The coupling between constructed wetlands and reservoir (CWs-R) afforded a novel ecosystem to improve the water quality and increase the emergency storage capacity of micro-polluted river drinking water source. In this study, spectroscopic characteristics of DOM in YL CWs-R ecosystem were first systematic studied based on a three-year field monitoring to investigate the chemical composition, sources and track the involved biogeochemical processes in the ecosystem. Three humic-like components (C1, C2, and C4, em >380 nm) and one protein-like component (C3, em < 380 nm) were identified by PARAFAC model. Significant spatiotemporal variations in concentration and composition of FDOM were observed in YL CWs-R ecosystem. The improved water transparency (SD) and, the increased hydraulic retention time (HRT) along YL CWs-R ecosystem enhance photochemical processes, leading to significant decreases in the intensities of humic-like components in effluent (P < 0.05) with lower degrees of aromaticity, molecular weights, and humification (decrease in HIX and increases in S and BIX). In contrast, no significant spatial difference was observed for protein-like component (P > 0.05), which implies that the biodegradation and production of protein-like component may balance each other in the CWs-R ecosystem. The ecological pond unit plays a major role in the removal and transformation of DOM, especially in summer, while wetland purification unit contributes little to DOM reduction. In addition, the decay of aquatic macrophytes in wetland purification unit and the risk of algal bloom in the ecological pond unit might become important autochthonous sources of DOM, especially in summer and autumn. These findings are critical for further understanding the transformation processes of DOM in large-scale CWs-R ecosystems, and could provide important implications to improve sustainable safety of drinking water sources.
人工湿地与水库(CWs-R)的耦合为改善水质和增加微污染河流饮用水源应急储存能力提供了一个新的生态系统。本研究基于三年野外监测,首次系统研究了 YL CWs-R 生态系统中 DOM 的光谱特征,以研究其化学组成、来源,并追踪生态系统中涉及的生物地球化学过程。通过 PARAFAC 模型鉴定了三种腐殖质类成分(C1、C2 和 C4,em >380nm)和一种蛋白质类成分(C3,em <380nm)。YL CWs-R 生态系统中 FDOM 的浓度和组成存在显著的时空变化。YL CWs-R 生态系统中透光率(SD)的提高和水力停留时间(HRT)的增加增强了光化学过程,导致流出物中腐殖质类成分的强度显著降低(P <0.05),芳香度、分子量和腐殖化程度降低(HIX 降低,S 和 BIX 增加)。相比之下,蛋白质类成分没有观察到显著的空间差异(P >0.05),这意味着在 CWs-R 生态系统中,蛋白质类成分的生物降解和产生可能相互平衡。生态池塘单元在 DOM 的去除和转化中起着主要作用,特别是在夏季,而湿地净化单元对 DOM 的减少贡献很小。此外,湿地净化单元中水生植物的衰减和生态池塘单元中藻类大量繁殖的风险可能成为 DOM 的重要内源来源,特别是在夏季和秋季。这些发现对于进一步了解大型 CWs-R 生态系统中 DOM 的转化过程具有重要意义,并可为提高饮用水源的可持续安全性提供重要启示。