胶州湾滨海湿地土壤溶解性有机质的三维荧光特性

为了了解滨海湿地土壤中溶解性有机质的结构特征及来源,2014年1月在胶州湾采集光滩、碱蓬、芦苇和大米草湿地的土壤样品,测定土壤溶解性有机质(DOM)含量,利用三维荧光技术进行光谱分析.结果表明: 胶州湾4种湿地类型土壤溶解性有机碳(DOC)含量表现为大米草湿地＞光滩＞碱蓬湿地＞芦苇湿地,垂直剖面上随土层深度的增加DOC含量均呈减少的趋势.经光谱分析,胶州湾湿地土壤DOM的三维荧光光谱(3DEEMs)中出现了B、T、A、D和C等5种荧光峰,分别代表类酪氨酸、类色氨酸、类富里酸、类可溶性微生物副产物和类腐殖酸5种组分.利用荧光区域积分(FRI)法对5种组分进行定量分析,类色氨酸、类富里酸和类酪氨酸在DOM各组分含量中居前3位,类可溶性微生物副产物和类腐殖酸的含量次之,二者含量差异不显著.DOM的5种组分相互之间均呈显著正相关,与DOC含量呈显著正相关,与总磷、有效磷、总氮有不同程度的相关性.胶州湾4种湿地类型土壤DOM主要由生物相互作用内源产生,且腐殖化程度较低.     

冻融条件和土壤湿度对森林土壤渗漏液溶解性有机质含量与光谱结构特征的影响

土壤溶解性有机质(DOM)含量及其稳定性影响土壤碳氮循环关键过程,目前气候变化下森林土壤DOM含量及其光谱结构特征仍不明确.本研究利用长白山阔叶红松混交林和次生白桦林表层土壤进行室内冻融模拟试验,结合三维荧光光谱-平行因子分析方法,研究冻融强度和冻融循环次数及其交互作用对不同湿度温带森林土壤渗漏液DOM含量、组分和光谱结构特征的影响.结果表明: 森林土壤渗漏液DOM含量及其组分因林分类型、土壤湿度、冻融强度、冻融循环次数不同而存在差异.2种林分土壤渗漏液DOM含量均在中湿度下最低,并受高强度冻融影响显著,且随冻融循环次数增加呈现先增加后降低的趋势.可鉴别DOM的3个荧光组分:胡敏酸类DOM、富里酸类DOM和蛋白类DOM;阔叶红松混交林土壤渗漏液DOM组分以富里酸类物质为主,腐殖化程度较高;而次生白桦林土壤渗漏液DOM组分以胡敏酸类物质为主,3组分受冻融强度显著影响,稳定性较低.经冗余分析(RDA)发现,林分在很大程度上决定森林土壤DOM属性变化,次生白桦林土壤渗漏液DOM含量及其3组分荧光强度大于阔叶红松混交林;土壤湿度显著影响DOM芳香性,2种林分土壤渗漏液DOM芳香性均呈中湿度>高湿度>低湿度的趋势;随冻融强度增加,阔叶红松混交林土壤渗漏液DOM芳香性显著降低;多次冻融循环显著提高2种林分土壤渗漏液DOM腐殖化程度.因此,不同冻融作用下,低湿度温带森林土壤渗漏液DOM含量及其生物有效性呈现增加的趋势,尤其是次生白桦林土壤,可能会增加春季冻融期温带森林土壤溶解性有机质淋溶损失.这些结果可为深入研究野外冻融期温带森林土壤溶解性有机质周转机制提供参考.     

冰川退缩区不同演替阶段土壤溶解性有机质光谱特征及环境响应

溶解有机质(DOM)作为土壤中最活跃的有机组分,在土壤生物地球化学过程中起着关键作用,探讨植被演替过程中DOM的来源、组成、环境响应与累积规律,对预测土壤碳循环过程具有重要意义。本研究从海螺沟冰川退缩区植被原生演替序列选取演替年龄分别为12、30、40、50、80、120年的样地采集表层和亚表层土壤样本,测定DOM浓度并进行紫外-可见光光谱和三维荧光光谱分析,研究原生演替过程中DOM含量和组成的变化特征及其影响因素。结果表明: 土壤DOM浓度随演替年龄的增加而显著增加。土壤DOM中类蛋白组分、荧光指数和生物指数随演替时间的增加而减小,类腐殖质组分和腐殖化程度随演替过程不断增加,土壤DOM芳香化程度先增加后减小。pH值、铵态氮含量解释了62.2%的表层土壤DOM组分变异,土壤含水率和pH值解释了64.3%的亚表层土壤DOM组分变异,说明环境因素是影响海螺沟冰川退缩区原生演替过程中土壤DOM数量和组成的重要因子。     

刚毛藻腐烂过程中溶解性有机物的释放和细菌群落的变化

通过室内培养模拟了高密度刚毛藻聚积腐烂过程,研究了刚毛藻在不同腐烂时间段下的溶解性有机物(DOM)的释放和附着微生物的群落变化。结果表明:在40d的分解实验中,刚毛藻生物量(干重)减少,且表现为前期损失快,后期损失减缓的趋势。在实验结束时(40d),干物质残留率为43.15%,质量损失了56.85%。在刚毛藻分解过程中, DOM在7—10d内快速释放达到最大值,而后降低。DOM的组分也变得复杂,荧光峰从区域Ⅰ、Ⅱ和Ⅳ逐渐转移到区域Ⅲ和Ⅴ。大量的简单芳香蛋白,如酪氨酸类物质被微生物转化为各种代谢物,并产生了腐殖质类物质。刚毛藻附着微生物优势菌为变形菌门(Proteobacteria)、拟杆菌门(Bacteroidetes)和厚壁菌门(Firmicutes),相对丰度分别为6.54%—71.62%、16.83%—55.50%和0.95%—20.91%。在腐烂过程的不同阶段中,微生物的组成差异显著,表现为前期主要是Proteobacteria占主导优势,实验后期是Bacteroidetes占主导优势,细菌群落的演替与DOM组成的变化相关。     

有机物质对土壤镉有效性的影响研究综述

土壤中的低分子有机酸和腐殖酸对镉的有效性有重要作用。根系分泌的低分子量有机酸能提高土壤镉的可提取率、移动性和生物有效性,但是更大分子量的有机酸EDTA却抑制植物对镉的吸收,腐殖酸促进土壤镉的溶解性;因腐殖酸组分和环境条件,腐殖酸能够促进也能抑制土壤镉活性,因此有必要深入研究影响腐殖酸固定镉的因素,以达到利用有机质抑制土壤镉活性的目的。     

黄山松土壤可溶性有机质对氮添加的响应及其与细菌群落的关联

为探究黄山松土壤可溶性有机质(DOM)数量和质量对短期氮(N)添加的响应及其与细菌群落的关联,在福建戴云山自然保护区设置不同N添加水平(0、40和80 kg N·hm^-2·a^-1)试验,采用三维荧光与平行因子联用法,并结合高通量测序手段分别对土壤DOM和细菌群落进行分析。结果表明: 与对照相比,N添加整体降低了0～10和10～20 cm土层可溶性有机碳(DOC)含量和DOM腐殖化指数(HIX),其中,高氮(80 kg N·hm^-2·a^-1)添加下均显著降低。平行因子分析法进一步表明N添加下DOM中类腐殖质组分(C1、C2)的相对含量降低。此外,N添加减少了富营养细菌(变形菌门、酸微菌纲)的相对丰度,而增加了贫营养细菌(斯巴达杆菌纲)的相对丰度。富营养细菌的相对丰度与HIX、C1、C2呈显著正相关,与相对易分解的类富里酸组分(C3)呈显著负相关;而贫营养细菌的情况则相反。说明N添加下不同生活策略的细菌类群对DOM中难分解和易分解组分存在明显的偏好性。我们推测N沉降加剧背景下土壤微生物生活策略的转变可能有助于DOM组分的塑造。     

氮磷汇入驱动下的河流轮虫群落演替

【目的】解析污染条件下河流生物区系的演替过程及机制,可以为生物多样性减少提供诊断,为生物多样性保护和水生生态系统的生态安全提供科学支撑。【方法】以对污染具有指示作用的轮虫类群为研究对象,选择覆盖京津冀地区的、受到人类活动干扰的北三河水系为研究区域,分别对该区域富营养化相关水质参数和轮虫群落组成进行分析,在解析污染物排放导致的河流水体水质差异和轮虫群落组成差异的基础上,阐明导致轮虫群落演替的关键污染因子。【结果】水体水质指标的分析结果表明,西部河流与东部诸河具有明显不同的环境条件,其氮、磷指标(包括总氮、溶解性总氮、总磷、溶解性总磷及活性磷)浓度显著增加。轮虫群落的分析结果表明,与东部诸河相比,西部河流的物种数目、生物个体数、物种丰度及香农威纳指数均显著降低,且群落组成显著差异。群落-环境相关分析显示,总氮、溶解性总氮、总磷、溶解性总磷、活性磷以及氨氮是导致群落显著差异的关键环境因子。【结论】北三河水系西部河流的氮、磷含量显著高于东北部河流;在环境条件改变的前提下,北三河水系西部河流比东部河流物种丰度、生物量均显著减少,同时群落组成也显著改变,高耐污型物种出现。氮、磷元素的输入是导致轮虫群落演替的关键环境因子。     

喀斯特湖泊-河流系统溶解性有机质光谱特征

为探索喀斯特湖泊-河流系统溶解性有机质(DOM)光谱特征空间格局,该研究以我国贵州红枫湖、百花湖和老马河为对象,分析了表层水体DOM紫外参数(SUVA₂₅₄、SUVA₂₈₀、S_275-295、S_350-400、S_R和E2/E3),利用三维荧光-平行因子(EEM-PARAFAC)解析DOM主要成分,同时基于荧光参数(HIX、FI、BIX和β：α)揭示其来源信息。该研究运用Spearman相关性分析及主成分分析(PCA)方法,揭示DOM参数的内在联系及重要组分贡献。结果显示,红枫湖、百花湖和老马河SUVA₂₅₄和SUVA₂₈₀值较低,而E2/E3、S_275-295和S_350-400值较高,说明芳香类成分占比较少且DOM整体分子量较小。水体DOM主要成分为:红枫湖/百花湖(C1:微生物代谢类腐殖质;C2:可见光范围腐殖质;C3:色氨酸),老马河(C1:色氨酸;C2:富里酸;C3:陆源类腐殖质)。水体BIX范围在0.77-1.12之间,说明生物源和陆源输入共同贡献DOM。红枫湖与百花湖FI值小于1.4,而老马河在1.4-1.9间,说明河流内源DOM贡献率高于湖泊。水体β：α值范围在0.73-1.10之间,说明新生DOM具有显著贡献。湖泊与河流HIX值低于4,表明水体腐殖化程度低。老马河HIX与S_R和S_275-295呈正相关(P ＜ 0.05)且与FI呈负相关(P ＜ 0.05),说明DOM腐殖化程度与分子大小和来源密切联系。芳香类DOM的同质性导致SUVA₂₅₄和SUVA₂₈₀相互耦合。研究发现新生DOM多具有生物降解性,表现为BIX和β：α强相关。相对于激流系统,湖泊具有更多的水力停留时间,这可能进一步促进内源微生物的代谢,导致生物驱动的有机质快速循环,因此不同DOM生物讯号相互耦合。研究阐明了喀斯特湖泊-河流系统DOM成分与来源特征,有望为研究全球碳循环过程提供数据支撑。     

水土保持林恢复土壤可溶性碳氮组分动态与三维荧光特征分析

为探究水土保持林恢复过程中土壤可溶性碳氮含量变化及其有机组成特性,揭示水保林土壤固存可溶性有机质的效应及机制。选取了黄土丘陵区恢复12-45a的人工柠条、刺槐林以及撂荒地,分析了土壤可溶性碳氮含量及其三维荧光光谱特征与特性参数的动态变化。结果表明：随恢复年限的增加,3种植被土壤可溶性有机碳（DOC）、有机氮（DON）、无机氮（DIN）的含量均呈增加趋势,并且相同恢复年限下DOC、DON、DIN含量总体表现为撂荒 < 柠条 < 刺槐;但柠条和刺槐林土壤DOC：DON及二者占总有机碳、全氮比例并未持续增加,到恢复45a时DOC占总有机碳比例以及DOC：DON均以撂荒地最高,刺槐林最低,DON占全氮比例则表现相反。三维荧光结合平行因子分析得出所有样地土壤可溶性有机质（DOM）主要有大分子腐殖物质（C1）、低分子量类富里酸（C2）、类色氨酸（C3）及农业措施输入的腐殖物质（C4）4个组分,并且以C1组分占比最大,平均达37.4%。随恢复年限增加,3种植被土壤DOM中C3组分占比升高,C2和C4组分占比降低,C1组分占比在柠条和刺槐林中升高,在撂荒地中则降低。不同植被土壤可溶性有机质荧光指数（FI）、新鲜度指数（β：α）及自生源指数（BIX）差异不显著,分别为1.63、0.58、0.59;不同恢复年限撂荒地腐殖化指数（HIX）没有差异,但柠条和刺槐林显著高于撂荒且随恢复年限增加先增大后稳定。综上,水保林持续恢复可以显著提升土壤可溶性碳氮含量,也使土壤可溶有机质组成趋向复杂和相对稳定,利于累积固持,特别以刺槐林效应最明显。     

径流雨水中溶解性有机质特征演化及其对典型污染物迁移和生物有效性的影响

地表径流污染已经逐渐成为城市面源污染的重要组成部分。其中溶解性有机质DOM (Dissolved organic matter)是有机污染物的主要组成部分。DOM中因为含有大量不饱和结构、官能团,其中包括羟基、羧基、羰基、胺基等,这些结构容易与径流中重金属结合发生络合反应,改变重金属的赋存形态,从而对其迁移转化及其生物有效性产生很大的影响。本文以北京市地表径流为研究对象,研究城市地表径流在冬、夏季不同功能区不同下垫面中溶解性有机质特征及其与典型重金属的作用机制,通过荧光淬灭滴定实验,研究夏季径流雨水中DOM的不同组分与重金属Cu~(2+)、Pb~(2+)、Zn~(2+)之间的结合机制。研究结果显示PARAFAC将获得的样品都分解成2类6个不同的组分,1种腐殖酸,1种类蛋白;类蛋白物质的荧光强度与Cu~(2+)、Pb~(2+)的淬灭率要强于腐殖酸,而Zn~(2+)则呈现相反趋势;通过使用二维相关同步光谱发现DOM对重金属Cu~(2+)、Pb~(2+)、Zn~(2+)的敏感性呈现递减趋势,二维相关异步光谱发现Cu~(2+)、Pb~(2+)会先与位于270—300nm附近类蛋白光谱带反应,Zn~(2+)则会先与330nm附近的腐殖酸光谱带反应。     

The influence of humic substances on the molecular weight distributions of phosphate and iron in epilimnetic lake waters

1. The influence of humic substances on the association of free inorganic iron and phosphate with material of larger molecular weight was investigated in epilimnetic samples from two humus‐rich lakes of contrasting ionic strength. After modification of the molecular weight distribution of the humic substances in the samples using dialysis and ultrafiltration, the molecular weight distribution of added radioisotopes ( Fe3+ and PO43?) was assessed using gel filtration chromatography.
2. The association of Fe3+ and PO43? with larger molecular weight fractions (>50 000 and 10 000–50 000 Da) was not in general related to the quantity of humic substances of the same molecular weight in the samples. However, the proportions of Fe3+ and PO43? observed in higher molecular weight peaks were strongly correlated to the quantity of humic substances of the same molecular weight in (a) the 10 000–50 000 Da peak in the sample of low ionic strength at pH 5.5 and pH 7.0, and (b) the> 50 000 Da peak in the sample of higher ionic strength at pH 4.0.
3. It was concluded that humic substances promote the association of Fe3+ and PO43? with higher molecular weight fractions primarily by acting as peptizing agents for inorganic colloids containing Fe and P. Association of Fe3+ and PO43? with material of higher molecular weight via the formation of humic substance‐Fe3+–PO43? complexes was identified but only at specific pH and within specific molecular weight ranges for each of the epilimnetic lake water samples studied.     

A large molecular size fraction of riverine high molecular weight dissolved organic matter (HMW DOM) stimulates growth of the harmful dinoflagellate Alexandrium minutum

An increase in the concentration of riverine dissolved organic matter (DOM) has been observed during the last decades, and this material can stimulate marine plankton in coastal waters with significant freshwater input. We studied the effect of two size fractions of riverine high molecular weight dissolved organic matter (HMW DOM), isolated with tangential ultrafiltration, on the harmful dinoflagellate Alexandrium minutum and a natural isolate of marine bacteria under laboratory conditions. Both A. minutum and bacteria grew significantly better with the low MW DOM compared to both the high MW DOM fraction and controls (no DOM additions). This experiment demonstrates that the harmful algae A. minutum and bacteria benefit from larger molecules of river HMW DOM, and highlights the potential of A. minutum to utilize organic nitrogen from large DOM molecules. This ability may enhance their likelihood of success in estuaries/costal waters with a humic rich freshwater input, especially when the relative amount of large molecules within DOM is more pronounced.     

Photooxidation of wetland and riverine dissolved organic matter: altered copper complexation and organic composition

In natural waters, the uptake of transition metals such as copper (Cu) by aquatic biota depends on the activity of the free cupric ion ({Cu²⁺}) rather than on total Cu concentration. Thus, an important ecological function of dissolved organic matter (DOM) in aquatic ecosystems is Cu–DOM complexation, which greatly decreases the {Cu²⁺}. However, Cu bioavailability is greatly modified by source and environmental history of DOM because DOM affinity for Cu varies by orders of magnitude among DOM sources; moreover, DOM is photochemically unstable. During 72-h irradiation experiments at intensities approximating sunlight with DOM from a palustrine wetland and a third-order river, we investigated photooxidative effects on DOM complexation of Cu as well as spectral and chemical changes in DOM that might explain altered Cu complexation. Irradiation decreased Cu complexation by riverine DOM, but unexpectedly increased Cu complexation by wetland DOM, resulting in 150% greater {Cu²⁺} in riverine DOM at the same dissolved organic carbon concentrations. The specific ultraviolet absorption (SUVa) and humic substances tracked photochemical changes in the conditional stability constants of Cu–DOM complexes, suggesting that the aromaticity of DOM influences its affinity for Cu. Carbonyl concentration in ¹³C nuclear magnetic resonance spectra (¹³C-NMR) covaried directly with Cu binding-site densities in DOM. However, no aspect of Cu–DOM complexation consistently covaried with fluorophores (i.e., the fluorescence index) or low molecular weight organic acids. Our results suggest that global increases in UV radiation will affect Cu–DOM complexation and subsequent Cu toxicity depending on light regime as well as DOM source. Handling editor: K. Martens     

Revealing Sources and Distribution Changes of Dissolved Organic Matter (DOM) in Pore Water of Sediment from the Yangtze Estuary

Dissolved organic matter (DOM) in sediment pore waters from Yangtze estuary of China based on abundance, UV absorbance, molecular weight distribution and fluorescence were investigated using a combination of various parameters of DOM as well as 3D fluorescence excitation emission matrix spectra (F-EEMS) with the parallel factor and principal component analysis (PARAFAC-PCA). The results indicated that DOM in pore water of Yangtze estuary was very variable which mainly composed of low aromaticity and molecular weight materials. Three humic-like substances (C1, C2, C4) and one protein-like substance (C3) were identified by PARAFAC model. C1, C2 and C4 exhibited same trends and were very similar. The separation of samples on both axes of the PCA showed the difference in DOM properties. C1, C2 and C4 concurrently showed higher positive factor 1 loadings, while C3 showed highly positive factor 2 loadings. The PCA analysis showed a combination contribution of microbial DOM signal and terrestrial DOM signal in the Yangtze estuary. Higher and more variable DOM abundance, aromaticity and molecular weight of surface sediment pore water DOM can be found in the southern nearshore than the other regions primarily due to the influence of frequent and intensive human activities and tributaries inflow in this area. The DOM abundance, aromaticity, molecular weight and fluorescence intensity in core of different depth were relative constant and increased gradually with depth. DOM in core was mainly composed of humic-like material, which was due to higher release of the sedimentary organic material into the porewater during early diagenesis.     

Characterization of Nanming River (southwestern China) sewerage-impacted pollution using an excitation-emission matrix and PARAFAC

Nanming River, the largest urban river in Guizhou Province, southwestern China plateau, has been severely polluted for decades. This study characterizes the organic materials and their sources in the upstream and downstream waters by dissolved organic carbon (DOC), excitation emission matrix (EEM) spectroscopy, parallel factor (PARAFAC) analysis and photo-microbial experiments. DOC concentrations were low (47–120 μM C) upstream and relatively high (146–462 μM C) downstream. The PARAFAC studies on the sample EEM spectra demonstrated that the upstream dissolved organic matter (DOM) was mostly composed of one component that had a fulvic acid-like substance; downstream DOM was composed of two components with mixtures of tryptophan-like and fulvic acid-like substances. From the results of the sewerage drainage samples collected along the bank of the river, it is evident that both household detergent-like and protein-like or tryptophan-like substances are predominantly present, indicating that untreated sewerage effluents are the major sources of organic matter pollution in Nanming River. The degradation experiments conducted on river, sewerage drainage and commercial detergent samples demonstrated that the detergent-like and tryptophan-like substances are both photochemically and microbiologically more decomposable than fulvic acid-like materials under sunlight and dark incubations. These results suggest that the input of the untreated sewerage effluents along the streams is the major pollution source in Nanming River, and the fluorescent DOM was efficiently affected by both photochemical and microbial processes.     

Characterisation and reactivity continuum of dissolved organic matter in forested headwater catchments of Andean Patagonia

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Uncoupling of Bacterial and Terrigenous Dissolved Organic Matter Dynamics in Decomposition Experiments

The biodegradability of terrigenous dissolved organic matter (tDOM) exported to the sea has a major impact on the global carbon cycle, but our understanding of tDOM bioavailability is fragmentary. In this study, the effects of preparative tDOM isolation on microbial decomposition were investigated in incubation experiments consisting of mesocosms containing mesohaline water from the Baltic Sea. Dissolved organic carbon (DOC) consumption, molecular DOM composition, bacterial activities, and shifts in bacterial community structure were compared between mesocosms supplemented with riverine tDOM, either as filtered, particle-free river water or as a concentrate obtained by lyophilization/tangential ultrafiltration, and those containing only Baltic Sea water or river water. As shown using ultra-high-resolution mass spectrometry (15 Tesla Fourier-transform ion cyclotron resonance mass spectrometry, FT-ICR-MS) covering approximately 4600 different DOM compounds, the three DOM preparation protocols resulted in distinct patterns of molecular DOM composition. However, despite DOC losses of 4–16% and considerable bacterial production, there was no significant change in DOM composition during the 28-day experiment. Moreover, tDOM addition affected neither DOC degradation nor bacterial dynamics significantly, regardless of the tDOM preparation. This result suggested that the introduced tDOM was largely not bioavailable, at least on the temporal scale of our experiment, and that the observed bacterial activity and DOC decomposition mainly reflected the degradation of unknown, labile, colloidal and low-molecular weight DOM, both of which escape the analytical window of FT-ICR-MS. In contrast to the different tDOM preparations, the initial bacterial inoculum and batch culture conditions determined bacterial community succession and superseded the effects of tDOM addition. The uncoupling of tDOM and bacterial dynamics suggests that mesohaline bacterial communities cannot efficiently utilize tDOM and that in subarctic estuaries other factors are responsible for the removal of imported tDOM.     

Dissolved organic matter quantity and quality from freshwater and saltwater lakes in east-central Alberta

Concentrations of dissolved organic matter (DOM) in surface waters of sub-humid to semi-arid lakes in east-central Alberta increase with increasing salinity and water residence time from about 20 to 330 mg L^–1 as dissolved organic carbon (DOC). This pattern is opposite to that observed among freshwater lakes spanning a gradient in water residence times, and is probably caused by evaporative concentration of refractory DOM. The proportion of total DOC, operationally defined as humic substances using XAD-8 resin, was high, though similar to surface waters typically referred to as "humic", and independent of salinity. Very long water residence times (hundreds of years) in saline lakes favors evapoconcentration of low-color, low molecular weight DOM, with N-content characteristic of allochthonous DOM.     

Distribution and characteristics of molecular size fractions of freshwater-dissolved organic matter in watershed environments: its implication to degradation

Distributions of molecular size and fluorescence properties of dissolved organic matter (DOM) in the Lake Biwa and Lake Baikal watersheds were investigated using the cross-flow ultrafiltration technique and three-dimensional fluorescence measurements. From the fluorescence properties, protein-like substances were usually found in the 0.1 μm-GF/F fraction (the Durapore membrane retentate of the GF/F filtrate) of the lake DOM. The results indicated autochthonous production of protein-like organic-matters in the lake environment. Fulvic acid (FA)-like components were composed of two fractions with respect to fluorescence properties and molecular size. Two FA-like fluorescence peaks, which showed different fluorescence peak positions in the excitation-emission matrix (EEM), were partly fractionated by the molecular size of 5000 daltons (5 kDa). The FA-like fluorescence peak position of the <5-kDa fraction was observed at the shorter wavelength region compared with that of the fraction between 5 kDa and 0.1 μm (5 kDa20.1 μm fraction). A blue shift of the FA-like fluorescence peak position as well as a decrease in the molecular size of the DOM was observed in lake samples. The relative contribution of the <5 kDa fraction to the DOC concentration was high in lake waters (68%–79%) compared with river waters (44%–68%), suggesting characteristic changes in molecular size between riverine and lacustrine DOM. DOM of the 5 kDa–0.1 μm fraction was relatively higher in river waters than in lake waters. These findings coincided with in situ distributions of the fluorescence properties and molecular size of DOM found in both stream and lake environments. These results indicate that FA-like substances from forested watersheds are decomposed qualitatively and quantitatively in the river-lake environment by photochemical and biological processes.     

Growth and survival of tadpoles (Bufo americanus) fed amorphous detritus derived from natural waters

Growth and survival of tadpoles (Bufo americanus) were used to assess the food value of three types of amorphous detritus thought to be derived from dissolved organic matter (DOM) transported in river water or groundwater: 1. Flocculent organic aggregates suspended at the mouth of a humic stained river which drains into Lake Superior; 2. Precipitates formed directly from humic stained river water; 3. The < 35 m fraction of littoral lake sediment. Tadpoles were unable to grow when fed the amorphous detritus, but experienced lower mortality than unfed animals. Although the food quality of certain types of detritus derived from DOM may be inadequate to support the growth of aquatic fine particle feeders it may contribute to the nutrition of facultative detritivores.