利用稳定同位素指纹图谱揭示封闭内陆湖悬浮颗粒和沉积物中有机物的来源

IF 4.3 3区 材料科学 Q1 ENGINEERING, ELECTRICAL & ELECTRONIC ACS Applied Electronic Materials Pub Date : 2024-04-16 DOI:10.1016/j.ijsrc.2024.04.004
Xiaohui Ren , Ruihong Yu , Jianfang Kang , Rui Wang , Xiangwei Li , Dalun Wang , Pengxuan Zhang
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引用次数: 0

摘要

悬浮颗粒和沉积物是湖泊中有机物(OM)的重要储存库,跟踪悬浮颗粒有机物(SPOM)和沉积物有机物(SOM)的形成是了解 OM 的环境行为和湖泊生态系统碳循环的关键。然而,很少有研究同时关注封闭内陆湖泊中 SPOM 和 SOM 的来源,以揭示它们之间的差异及其对水质的影响。本研究基于稳定碳(δC)和氮(δN)同位素组成,对中国北方典型的封闭内陆湖--岱海湖春、夏、秋三季SPOM和SOM的来源进行了研究。结果表明,SPOM 的 δC 和 δN(POC 和 PN 分别表示颗粒有机碳和有机氮)的变化范围分别为-30.99‰至-21.71‰和 1.43‰至 9.47‰。SPOM 主要来源于污水、土壤和浮游植物,平均贡献率分别为 29.5%、27.7% 和 19%,各 SPOM 来源的空间变化较小。不过,浮游植物的贡献率从春季到夏季呈下降趋势,而土壤的贡献率则呈相反变化。SOM的δC和δN(其中TOC和TN分别指有机碳总量和氮总量)分别在-26.41‰至-23.99‰和3.3‰至7.66‰之间变化。土壤和污水是 SOM 的主要来源,平均贡献率分别为 43.3% 和 27.8%,且各来源的时空变化较小。SPOM 和 SOM 来源的差异表明,浮游植物产生的 SPOM 易于降解,而污水和土壤产生的 SPOM 则倾向于沉积在湖泊沉积物中。此外,SPOM 对水质的影响明显超过 SOM。SPOM 的来源特征与水体富营养化和盐度指标相关,这对水质有重要影响。这些同位素证据表明,外源输入是封闭内陆湖 OM 的主要来源,但 SPOM 和 SOM 的来源特征存在一些差异。
本文章由计算机程序翻译,如有差异,请以英文原文为准。

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Unraveling the sources of organic matter in suspended particulates and sediment in a closed inland lake using stable isotope fingerprinting

Suspended particulates and sediment are significant reservoirs of organic matter (OM) in lakes, and tracking the formation of suspended particulate organic matters (SPOMs) and sediment organic matters (SOMs) is the key to understanding the environmental behavior of OM and the carbon cycling of lake ecosystems. However, few studies have simultaneously focused on the sources of SPOM and SOM in closed inland lakes to reveal their differences and implications for water quality. The current study investigated the sources of SPOM and SOM in Daihai Lake, a typical closed inland lake in northern China, based on stable carbon (δ13C) and nitrogen (δ15N) isotopic compositions, during spring, summer, and autumn. The results showed that δ13CPOC and δ15NPN (where POC and PN denote particulate organic carbon and nitrogen, respectively) of SPOM varied from −30.99‰ to −21.71‰ and 1.43‰–9.47‰, respectively. SPOM mainly originated from sewage, soil, and phytoplankton, with average contributions of 29.5%, 27.7%, and 19%, respectively, and each source of SPOM showed low spatial variation. However, the contribution of phytoplankton showed a decreasing trend from spring to summer, while the contribution of soil showed the opposite change. δ13CTOC and δ15NTN (where TOC and TN denote total organic carbon and nitrogen, respectively) of SOM varied from −26.41‰ to −23.99‰ and 3.3‰–7.66‰, respectively. Soil and sewage were the major sources of SOM, with average contributions of 43.3% and 27.8%, respectively, and each source showed small temporal and spatial variations. The differences between sources of SPOM and SOM revealed that phytoplankton-derived SPOM was easily degraded, whereas sewage- and soil-derived SPOM tended to deposit in the lake sediment. Additionally, the impact of SPOM on water quality significantly exceeded that of SOM. The source characteristics of SPOM were correlated with eutrophication and salinity indicators in the water, which have important implications for water quality. This isotopic evidence revealed that exogenous inputs were the main sources of OM in closed inland lakes, but there were some differences in the source characteristics between SPOM and SOM.

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