2017
DOI: 10.1016/j.watres.2017.04.006
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Molecular size-dependent abundance and composition of dissolved organic matter in river, lake and sea waters

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Cited by 200 publications
(81 citation statements)
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“…As expected, the three CDOM components and SUVA 254 showed a general decrease from Groups I to II, and then to Group III, whereas S 275–295 and the bulk DOC showed an opposite trend (Figure ). These trends verify our hypothesis and also suggest that different DOM components within the bulk DOM pool clearly had different mixing behaviors and environmental fate during their estuarine mixing and offshore transport, showing a heterogeneous nature of DOM pool in aquatic environments as reported in previous studies (e.g., Stolpe et al, ; Wang et al, ; Xu & Guo, ). Using field‐flow fractionation techniques capable of simultaneous size separation and characterization, Zhou et al () also observed distinct mixing behaviors among different sized humic‐like DOM components in the Bay St. Louis‐Mississippi Sound estuarine system.…”
Section: Discussionsupporting
confidence: 91%
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“…As expected, the three CDOM components and SUVA 254 showed a general decrease from Groups I to II, and then to Group III, whereas S 275–295 and the bulk DOC showed an opposite trend (Figure ). These trends verify our hypothesis and also suggest that different DOM components within the bulk DOM pool clearly had different mixing behaviors and environmental fate during their estuarine mixing and offshore transport, showing a heterogeneous nature of DOM pool in aquatic environments as reported in previous studies (e.g., Stolpe et al, ; Wang et al, ; Xu & Guo, ). Using field‐flow fractionation techniques capable of simultaneous size separation and characterization, Zhou et al () also observed distinct mixing behaviors among different sized humic‐like DOM components in the Bay St. Louis‐Mississippi Sound estuarine system.…”
Section: Discussionsupporting
confidence: 91%
“…As expected, the three CDOM components and SUVA 254 showed a general decrease from Groups I to II, and then to Group III, whereas S 275-295 and the bulk DOC showed an opposite trend (Figure 8). These trends verify our hypothesis and also suggest that different DOM components within the bulk DOM pool clearly had different mixing behaviors and environmental fate during their estuarine mixing and offshore transport, showing a heterogeneous nature of DOM pool in aquatic environments as reported in previous studies (e.g., Stolpe et al, 2014;Wang et al, 2010;Xu & Guo, 2017…”
Section: Comparisons Between Surface and Bottom Layerssupporting
confidence: 91%
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“…There is little information on the size distribution of coloured DOM (CDOM) in ocean waters 43–45 . Here we observed that the aLMW fraction hosts more humic- and protein-like fluorescence intensity per carbon unit than the aHMW DOM fraction (Fig.…”
Section: Resultsmentioning
confidence: 99%
“…DOM can directly affect nutrient cycling [4], the toxicity of organic pollutants [5], the solubility of heavy metals [6] and the aquatic ecosystem [5,7], and also indirectly influence the atmospheric CO 2 level and global climate change [8,9]. It is well known that DOM is a complex mixture of natural organic compounds found in various kinds of water bodies including rivers, lakes, glaciers, and oceans [10][11][12]. …”
Section: Introductionmentioning
confidence: 99%