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Spectroscopic characterization of dissolved organic matter isolates from sediments and the association with phenanthrene binding affinity

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dc.contributor.authorHur, Jin-
dc.contributor.authorLee, Bo-Mi-
dc.contributor.authorShin, Kyung-Hoon-
dc.date.accessioned2021-06-22T22:43:48Z-
dc.date.available2021-06-22T22:43:48Z-
dc.date.created2021-01-21-
dc.date.issued2014-09-
dc.identifier.issn0045-6535-
dc.identifier.urihttps://scholarworks.bwise.kr/erica/handle/2021.sw.erica/21969-
dc.description.abstractIn this study, selected spectroscopic characteristics of sediment organic matter (SOM) were compared and discussed with respect to their different isolation methods, the source discrimination capabilities, and the association with the extent of phenanthrene binding. A total of 16 sediments were collected from three categorized locations including a costal lake, industrial areas, and upper streams, each of which is likely influenced by the organic sources of algal production, industrial effluent, and terrestrial input, respectively. The spectroscopic properties related to aromatic structures and terrestrial humic acids were more pronounced for alkaline extractable organic matter (AEOM) isolates than for the SOM isolates based on water soluble extracts and pore water. The three categorized sampling locations were the most differentiated in the AEOM isolates, suggesting AEOM may be the most representative SOM isolates in terms of describing the chemical properties and the organic sources of SOM. Parallel factor analysis (PARAFAC) based on fluorescence excitation-emission matrix (EEM) showed that a combination of three fluorescent groups could represent all the fluorescence features of SOM. The three categorized sampling locations were well discriminated by the percent distributions of humic-like fluorescent groups of the AEOM isolates. The relative distribution of terrestrial humic-like fluorophores was well correlated with the extent of phenanthrene binding (r = 0.571; p < 0.05), suggesting that the presence of humic acids in SOM may contribute to the enhancement of binding with hydrophobic organic contaminants in sediments. Principal component analysis (PCA) further demonstrated that the extent of SOM's binding affinity might be affected by the degree of biogeochemical transformation in SOM. (C) 2014 Elsevier Ltd. All rights reserved.-
dc.language영어-
dc.language.isoen-
dc.publisherPergamon Press Ltd.-
dc.titleSpectroscopic characterization of dissolved organic matter isolates from sediments and the association with phenanthrene binding affinity-
dc.typeArticle-
dc.contributor.affiliatedAuthorShin, Kyung-Hoon-
dc.identifier.doi10.1016/j.chemosphere.2014.04.018-
dc.identifier.scopusid2-s2.0-84903577527-
dc.identifier.wosid000339601600060-
dc.identifier.bibliographicCitationChemosphere, v.111, pp.450 - 457-
dc.relation.isPartOfChemosphere-
dc.citation.titleChemosphere-
dc.citation.volume111-
dc.citation.startPage450-
dc.citation.endPage457-
dc.type.rimsART-
dc.type.docTypeArticle-
dc.description.journalClass1-
dc.description.isOpenAccessN-
dc.description.journalRegisteredClassscie-
dc.description.journalRegisteredClassscopus-
dc.relation.journalResearchAreaEnvironmental Sciences & Ecology-
dc.relation.journalWebOfScienceCategoryEnvironmental Sciences-
dc.subject.keywordPlusEXCITATION-EMISSION MATRIX-
dc.subject.keywordPlusFLUORESCENCE SPECTROSCOPY-
dc.subject.keywordPlusHUMIC SUBSTANCES-
dc.subject.keywordPlusSORPTION-
dc.subject.keywordPlusWATER-
dc.subject.keywordPlusFRACTIONS-
dc.subject.keywordPlusPYRENE-
dc.subject.keywordPlusACID-
dc.subject.keywordPlusLAKE-
dc.subject.keywordPlusHETEROGENEITY-
dc.subject.keywordAuthorSediment organic matter-
dc.subject.keywordAuthorAlkaline extractable organic matter-
dc.subject.keywordAuthorSource discrimination-
dc.subject.keywordAuthorOrganic carbon-normalized binding coefficient-
dc.subject.keywordAuthorHydrophobic organic contaminants (HOCs)-
dc.subject.keywordAuthorParallel factor analysis (PARAFAC)-
dc.identifier.urlhttps://www.sciencedirect.com/science/article/pii/S0045653514004846?via%3Dihub-
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