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[泗林水库中荧光溶解有机物的来源、特征及转化动力学]

[Sources, Characteristics and Transformation Dynamics of Fluorescent Dissolved Organic Matter in the Silin Reservoir].

作者信息

Lao Xin-Yu, Yuan Jie, Liu Yu, Khan M G Mostofa

机构信息

Institute of Surface-Earth System Science, Tianjin University, Tianjin 300072, China.

Key Laboratory of Earth and Planetary Physics, Institute of Geology and Geophysics, Chinese Academy of Sciences, Beijing 100029, China.

出版信息

Huan Jing Ke Xue. 2019 Mar 8;40(3):1209-1216. doi: 10.13227/j.hjkx.201807268.

DOI:10.13227/j.hjkx.201807268
PMID:31087967
Abstract

The aim of this study was to examine the sources and characteristics of various fluorescent dissolved organic matter (FDOM) components as well as their transformation dynamics. FDOM was determined in the incoming, surface (0 m), deeper (20 m), and outflowing waters of the Silin Reservoir in winter (January), spring (April), summer (June), and autumn (October) using excitation-emission matrix (EEM) spectra coupled with parallel factor (PARAFAC), EEM-PARAFAC modelling. The EEM-PARAFAC modelling results demonstrated that dissolved organic matter (DOM) in the Silin Reservoir waters was composed of three fluorescent components. These included terrestrial humic-like substances (C type) of terrestrial origin (component 1), microbial humic-like substances (M type) of phytoplankton origin (component 2), and protein-like or tryptophan-like or tyrosine-like (component 3) of phytoplankton origin. In addition, the terrestrial humic-like substances (C type) was identified from two fluorescence peaks (peak C at /=305-355/414-458 nm and peak A at / 245-270/414-458 nm) while the microbial humic-like substances (M type) was identified from peaks that included peak M at / 280-305/380-398 nm and peak A 230-235/380-417 nm. Similarly, protein-like or tryptophan-like or tyrosine-like components were also detected from two fluorescence peaks, including peak T 270-285/316-354 nm and peak T 225-230/316-354 nm. The fluorescence intensity of terrestrial humic-like substances gradually decreased in incoming waters to surface (0 m), deeper (20 m), and subsequently, in outflowing waters. This indicates the gradual degradation of the humic-like substances and their recalcitrant nature during water transport during the incoming-surface-deeper-outflowing water cycle in both summer and winter seasons by numerous environmental factors. These included photochemical, microbial, and dam barrier-affected physical processes. Conversely, from the fluorescence intensity results of microbial humic-like substances (M type), production or partial (in some cases complete) degradation in surface-deeper-outflowing waters, fluctuated. This suggests that microbial humic-like substances are autochthonously produced from phytoplankton, but are highly labile in response to photochemical, microbial, and dam barrier-affected physical processes. From the fluorescence intensity results of protein-like or tryptophan-like or tyrosine-like substances, it demonstrated that they were newly produced in surface (0 m) waters in the summer season, but in the winter season they were significantly produced in both surface and deeper waters of the reservoir, and then decreased in the outflowing waters. This suggests that protein-like or tryptophan-like or tyrosine-like substances are autochthonously produced by phytoplankton that simultaneously reproduced and then were degraded in surface and deeper waters by photochemical, microbial, and dam barrier-affected physical processes. These results therefore imply that the FDOM components identified by EEM-PARAFAC modelling are crucial to better understand the source characteristics of bulk DOM, its transformation mechanisms, and its the dynamics in a reservoir water system.

摘要

本研究的目的是研究各种荧光溶解有机物(FDOM)组分的来源和特征及其转化动态。利用激发-发射矩阵(EEM)光谱结合平行因子(PARAFAC)模型,对西林水库冬季(1月)、春季(4月)、夏季(6月)和秋季(10月)的入库水、表层水(0米)、深层水(20米)和出库水中的FDOM进行了测定。EEM-PARAFAC模型结果表明,西林水库水体中的溶解有机物(DOM)由三种荧光组分组成。这些组分包括陆源腐殖质类物质(C型)(组分1)、浮游植物源微生物腐殖质类物质(M型)(组分2)以及浮游植物源蛋白质类或色氨酸类或酪氨酸类物质(组分3)。此外,陆源腐殖质类物质(C型)可从两个荧光峰(/=305-355/414-458纳米处的C峰和/ 245-270/414-458纳米处的A峰)中识别出来,而微生物腐殖质类物质(M型)可从包括/ 280-305/380-398纳米处的M峰和/ 230-235/380-417纳米处的A峰等峰中识别出来。同样,蛋白质类或色氨酸类或酪氨酸类组分也可从两个荧光峰中检测到,包括/ 270-285/316-354纳米处的T峰和/ 225-230/316-354纳米处的T峰。陆源腐殖质类物质的荧光强度在入库水到表层水(0米)、深层水(20米),随后在出库水中逐渐降低。这表明在夏季和冬季的入库-表层-深层-出库水循环过程中,腐殖质类物质在水体输送过程中受到多种环境因素的影响而逐渐降解,且具有难降解的性质。这些因素包括光化学、微生物和大坝屏障影响的物理过程。相反,从微生物腐殖质类物质(M型)的荧光强度结果来看,其在表层-深层-出库水中的产生或部分(在某些情况下完全)降解情况存在波动。这表明微生物腐殖质类物质是由浮游植物自源产生的,但在光化学、微生物和大坝屏障影响的物理过程作用下高度不稳定。从蛋白质类或色氨酸类或酪氨酸类物质的荧光强度结果来看,表明它们在夏季表层(0米)水中新产生,但在冬季,它们在水库的表层和深层水中均大量产生,然后在出库水中减少。这表明蛋白质类或色氨酸类或酪氨酸类物质是由浮游植物自源产生的,浮游植物同时繁殖,然后在表层和深层水中通过光化学、微生物和大坝屏障影响的物理过程被降解。因此,这些结果意味着通过EEM-PARAFAC模型识别出的FDOM组分对于更好地理解水体DOM的来源特征、其转化机制及其在水库水系统中的动态至关重要。

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