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dc.contributor.authorKo, Young-Jin-
dc.contributor.authorChoi, Keunsu-
dc.contributor.authorLee, Soonjae-
dc.contributor.authorJung, Kyung-Won-
dc.contributor.authorHong, Seokwon-
dc.contributor.authorMizuseki, Hiroshi-
dc.contributor.authorChoi, Jae-Woo-
dc.contributor.authorLee, Wook-Seong-
dc.date.accessioned2024-01-19T21:32:04Z-
dc.date.available2024-01-19T21:32:04Z-
dc.date.created2021-09-05-
dc.date.issued2018-11-
dc.identifier.issn0043-1354-
dc.identifier.urihttps://pubs.kist.re.kr/handle/201004/120744-
dc.description.abstractChromate is considered a toxic contaminant in various water sources because it poses a risk to animal and human health. To meet the stringent limits for chromium in water and wastewater, pyrrolic nitrogen structure was investigated as a chromate adsorbent for aqueous solutions, employing a polypyrrole coating on carbon black. The characteristics of the adsorbent were analyzed by high-resolution transmission electron microscopy, energy-filtered transmission electron microscopy, and X-ray photoelectron spectroscopy. Chromate was adsorbed as both Cr(III) and Cr(VI). The chromate adsorption capacity increased (from 50.84 to 174.81 mg/g) with increasing amounts of pyrrole monomers (from 50 to 86%) in the adsorbent. The adsorption capacity was well-correlated with the pyrrolic nitrogen content (from 2.06 to 6.57 at%) in the adsorbent, rather than other types of nitrogen. The optimized adsorption capacity (174.81 mg/g in the equilibrium batch experiment and 211.10 mg/g at an initial pH of 3) was far superior to those of conventional adsorbents. We investigated the mechanism behind this powerful chromate adsorption on pyrrolic nitrogen via physical/chemical analyses of the pH-dependent adsorption behavior, supported by first-principles calculation based on density functional theory. We found that Cr(III) and Cr(VI) adsorption followed different reaction paths. Cr(III) adsorption occurred in two sequential steps: 1) A Jones oxidation reaction (JOR)-like reaction of Cr(VI) with pyrrolic N that generates Cr(III), and 2) Cr(III) adsorption on the deprotonated pyrrolic N through Cr(III) N covalent bonding. Cr(VI) adsorption followed an alternative path: hydrogen-bonding to the deprotonation-free pyrrolic N sites. The pH-dependent fractional deprotonation of the pyrrolic N sites by the JOR-like reaction in the presence of chromate played an important role in the adsorption. (C) 2018 Elsevier Ltd. All rights reserved.-
dc.languageEnglish-
dc.publisherElsevier BV-
dc.titleStrong chromate-adsorbent based on pyrrolic nitrogen structure: An experimental and theoretical study on the adsorption mechanism-
dc.typeArticle-
dc.identifier.doi10.1016/j.watres.2018.08.033-
dc.description.journalClass1-
dc.identifier.bibliographicCitationWater Research, v.145, pp.287 - 296-
dc.citation.titleWater Research-
dc.citation.volume145-
dc.citation.startPage287-
dc.citation.endPage296-
dc.description.isOpenAccessN-
dc.description.journalRegisteredClassscie-
dc.description.journalRegisteredClassscopus-
dc.identifier.wosid000449137700028-
dc.identifier.scopusid2-s2.0-85053125903-
dc.relation.journalWebOfScienceCategoryEngineering, Environmental-
dc.relation.journalWebOfScienceCategoryEnvironmental Sciences-
dc.relation.journalWebOfScienceCategoryWater Resources-
dc.relation.journalResearchAreaEngineering-
dc.relation.journalResearchAreaEnvironmental Sciences & Ecology-
dc.relation.journalResearchAreaWater Resources-
dc.type.docTypeArticle-
dc.subject.keywordPlusHEXAVALENT CHROMIUM-
dc.subject.keywordPlusAQUEOUS-SOLUTIONS-
dc.subject.keywordPlusWASTE-WATER-
dc.subject.keywordPlusVALUABLE METALS-
dc.subject.keywordPlusREMOVAL-
dc.subject.keywordPlusCARBON-
dc.subject.keywordPlusSURFACE-
dc.subject.keywordPlusREDUCTION-
dc.subject.keywordPlusRECOVERY-
dc.subject.keywordPlusKINETICS-
dc.subject.keywordAuthorChromate adsorption-
dc.subject.keywordAuthorPyrrolic nitrogen-
dc.subject.keywordAuthorJones oxidation-
dc.subject.keywordAuthorPolarization screening-
dc.subject.keywordAuthorFirst-principles calculation-
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