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dc.creatorSuručić, Ljiljana T.
dc.creatorSandić, Zvjezdana
dc.creatorStanković, Aljoša
dc.creatorJanjić, Goran
dc.creatorTadić, Tamara
dc.creatorMarković, Bojana
dc.creatorOnjia, Antonije
dc.date.accessioned2023-12-04T14:47:29Z
dc.date.available2023-12-04T14:47:29Z
dc.date.issued2023
dc.identifier.issn2637-3298
dc.identifier.urihttps://cer.ihtm.bg.ac.rs/handle/123456789/7000
dc.description.abstractThe contamination of water with chromium is a global issue that is especially severe in developing countries with intensive mining and heavy industry (South Africa, Pakistan, and India) [1,2]. Trivalent Cr(III) and hexavalent Cr(VI) are the most common forms found in effluent water. Whereas trivalent chromium is a micronutrient (25–35 g/day) involved in the metabolism of lipids and carbohydrates [3,4], hexavalent chromium is exceedingly toxic, teratogenic, and mutagenic. Particularly concerning are its high solubility in water, mobility in detritus, and potential for bioaccumulation in living tissues. Due to these factors, hexavalent chromium has been the subject of numerous studies, especially its removal from effluent [5,6]. These studies have demonstrated that sorption is a highly effective and relatively simple technique for chromium removal from wastewater. In terms of this, magnetic heavy metals nanosorbents derived from inorganic compounds and polymers [7-9] are incredibly intriguing, because they could have been readily extracted from the mixture using an external magnetic field. The sorption investigation of hexavalent chromium in aqueous solutions on the magnetic aminofunctionalized polymer nanocomposite based on glycidyl methacrylate, m-PGMA revealed its highly selectivity and efficiency. [10,11]. The binding mechanism of hexavalent chromium ions onto m-PGMA was investigated using kinetic, equilibrium, and thermodynamic experiments as well as molecular modeling techniques (theoretical quantum-chemical calculations) [12-15]. It was observed that the process occurs in two phases. In the first phase, electrostatic interactions attract hexavalent chromium ions to the surface of the sorbent via the active sites (amino and APTMS groups). Cr(VI) is then converted to Cr(III) ions, which can coordinate with amino or hydroxyl groups on the surface of the sorbent [16]. The trivalent chromium ions that persist in the solution or on the surface of the sorbent are less hazardous than the initial hexavalent form. The application of m-PGMA sorbent enables the transformation of the toxic form of chromium into a less hazardous form, which is significant due to the possibility of sorbent regeneration and the subsequent processing of the solution following sorption.sr
dc.language.isoensr
dc.publisherBanja Luka, Republic of Srpska, B&H : University PIMsr
dc.relationinfo:eu-repo/grantAgreement/MESTD/inst-2020/200026/RS//sr
dc.relationinfo:eu-repo/grantAgreement/MESTD/inst-2020/200135/RS//sr
dc.rightsopenAccesssr
dc.rights.urihttps://creativecommons.org/licenses/by/4.0/
dc.sourceThe Book of Abstracts - XII International conference on Social and Technological Development – STED 2023, June, 15-18, 2023, Trebinje / Zbornik izvoda radova - XII međunarodna konferencija o društvenom i tehnološkom razvoju – STED 2023, 15-18. juni 2023. godine, trebinjesr
dc.subjecthexavalent chromiumsr
dc.subjectsorptionsr
dc.subjectmagnetic polymer nanocompositesr
dc.titleReductive removal of hexavalent chromium in aqueous solution by magnetic amino-functionalized polymer nanocompositesr
dc.typeconferenceObjectsr
dc.rights.licenseBYsr
dc.citation.spage118
dc.citation.epage120
dc.citation.rankM34
dc.citation.rankM34
dc.identifier.rcubhttps://hdl.handle.net/21.15107/rcub_cer_7000
dc.identifier.fulltexthttp://cer.ihtm.bg.ac.rs/bitstream/id/27677/bitstream_27677.pdf
dc.type.versionpublishedVersionsr


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