Taihu Lake Laboratory Ecosystem Research Station, State Key Laboratory of Lake Science and Environment, Nanjing Institute of Geography and Limnology, Chinese Academy of Sciences, 73 East Beijing Road, Nanjing, China.
Water Res. 2009 Oct;43(18):4685-97. doi: 10.1016/j.watres.2009.07.024. Epub 2009 Jul 25.
Eight field campaigns in the eutrophic, shallow, Lake Taihu in the summers from 2005 to 2007, and a phytoplankton degradation experiment of 33 days, were carried out to determine the contribution of phytoplankton degradation to CDOM. Significant and positive correlations were found between the CDOM absorption coefficient at 355 nm [a(CDOM)(355)], normalized fluorescence emission (QSU) at 450 nm from excitation at 355 nm [F(n)(355)], and the chlorophyll a (Chla) concentration for all eight field campaigns, which indicates that the decomposition and degradation of phytoplankton is an important source of CDOM. In the degradation experiment, the CDOM absorption coefficient increased as phytoplankton broke down during the first 12 days, showing the production of CDOM from phytoplankton. After 12 days, a(CDOM)(355) had increased from the initial value 0.41+/-0.03 m(-1) to 1.37+/-0.03 m(-1) (a 234% increase), and the Chla concentration decreased from the initial value of 349.1+/-11.2 microg/L to 30.4+/-13.2 microg/L (a 91.3% decrease). The mean daily production rate of CDOM from phytoplankton was 0.08 m(-1) for a(CDOM)(355). Parallel Factor Analysis (PARAFAC) was used to assess CDOM composition from EEM spectra, and four components were identified: a terrestrial-like humic component, two marine-like humic components, and a protein-like component. The rapid increase in marine-like humic fluorophores (C3 and C4) during the degradation experiment suggests that in situ production of CDOM plays an important role in the dynamics of CDOM. The field campaigns and experimental data in the present study show that phytoplankton can be one of the important CDOM producers in eutrophic shallow lakes.
2005 年至 2007 年夏季,在富营养化、浅湖太湖进行了 8 次野外考察和 33 天的浮游植物降解实验,以确定浮游植物降解对 CDOM 的贡献。所有 8 次野外考察均发现,355nm 处的 CDOM 吸收系数[a(CDOM)(355)]、355nm 激发时归一化荧光发射(QSU)在 450nm 处的荧光强度[F(n)(355)]与叶绿素 a(Chla)浓度之间存在显著正相关,表明浮游植物的分解和降解是 CDOM 的重要来源。在降解实验中,在最初的 12 天内,随着浮游植物的分解,CDOM 吸收系数增加,表明 CDOM 是由浮游植物产生的。12 天后,a(CDOM)(355)从初始值 0.41+/-0.03 m(-1)增加到 1.37+/-0.03 m(-1)(增加 234%),Chla 浓度从初始值 349.1+/-11.2μg/L降低到 30.4+/-13.2μg/L(降低 91.3%)。浮游植物产生 CDOM 的日平均速率为 0.08 m(-1)。平行因子分析(PARAFAC)用于评估 EEM 光谱中的 CDOM 组成,共鉴定出四个组分:一个类腐殖质的陆源组分、两个类腐殖质的海洋组分和一个类蛋白质的组分。在降解实验过程中,海洋类腐殖质荧光团(C3 和 C4)的快速增加表明,原位 CDOM 的产生在 CDOM 的动态变化中起着重要作用。本研究中的野外考察和实验数据表明,浮游植物可能是富营养化浅水湖泊中重要的 CDOM 产生源之一。