Characterization of the Physical, Chemical, and Adsorption Properties of Coal-Fly-Ash–Hydroxyapatite Composites
(1) Hydroxyapatite (HAp), which can be obtained by several methods, is known to be a good adsorbent. Coal fly ash (CFA) is a commonly reused byproduct also used in environmental applications as an adsorbent. We sought to answer the following question: Can CFA be included in the method of HAp wet syn...
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doaj-cb2d463bb24d451da0d1ba0c2abb655c2021-07-23T13:56:00ZengMDPI AGMinerals2075-163X2021-07-011177477410.3390/min11070774Characterization of the Physical, Chemical, and Adsorption Properties of Coal-Fly-Ash–Hydroxyapatite CompositesEleonora Sočo0Dorota Papciak1Magdalena M. Michel2Dariusz Pająk3Andżelika Domoń4Bogdan Kupiec5Department of Inorganic and Analytical Chemistry, Faculty of Chemistry, Rzeszów University of Technology, 35-959 Rzeszów, PolandDepartment of Water Purification and Protection, Faculty of Civil, Environmental Engineering and Architecture, Rzeszów University of Technology, 35-959 Rzeszów, PolandInstitute of Environmental Engineering, Warsaw University of Life Sciences-SGGW, 02-787 Warsaw, PolandDepartment of Casting and Welding, Faculty of Mechanical Engineering and Aeronautics, Rzeszów University of Technology, 35-959 Rzeszów, PolandDepartment of Water Purification and Protection, Faculty of Civil, Environmental Engineering and Architecture, Rzeszów University of Technology, 35-959 Rzeszów, PolandDepartment of Casting and Welding, Faculty of Mechanical Engineering and Aeronautics, Rzeszów University of Technology, 35-959 Rzeszów, Poland(1) Hydroxyapatite (HAp), which can be obtained by several methods, is known to be a good adsorbent. Coal fly ash (CFA) is a commonly reused byproduct also used in environmental applications as an adsorbent. We sought to answer the following question: Can CFA be included in the method of HAp wet synthesis to produce a composite capable of adsorbing both heavy metals and dyes? (2) High calcium lignite CFA from the thermal power plant in Bełchatów (Poland) was used as the base to prepare CFA–HAp composites. Four types designated CFA–HAp1–4 were synthesized via the wet method of in situ precipitation. The synthesis conditions differed in terms of the calcium reactants used, pH, and temperature. We also investigated the equilibrium adsorption of Cu(II) and rhodamine B (RB) on CFA–HAp1–4. The data were fitted using the Langmuir, Freundlich, and Redlich–Peterson models and validated using <i>R<sup>2</sup></i> and <i>χ</i><sup>2</sup>/<i>DoF</i>. Surface changes in CFA–HAp2 following Cu(II) and RB adsorption were assessed using SEM, SE, and FT-IR analysis. (3) The obtained composites contained hydroxyapatite (Ca/P 1.67) and aluminosilicates. The mode of Cu(II) and RB adsorption could be explained by the Redlich–Peterson model. The CFA–HAp2 obtained using CFA, Ca(NO<sub>3</sub>)<sub>2</sub>, and (NH<sub>4</sub>)<sub>2</sub>HPO<sub>4</sub> at RT and pH 11 exhibited the highest maximal adsorption capacity: 73.6 mg Cu/g and 87.0 mg RB/g. (4) The clear advantage of chemisorption over physisorption was indicated by the Cu(II)–CFA–HAp system. The RB molecules present in the form of uncharged lactone were favorably adsorbed even on strongly deprotonated CFA–HAp surfaces.https://www.mdpi.com/2075-163X/11/7/774wet preparation methodchemical engineeringdye and heavy metals sorptionindustrial wastewater treatment |
collection |
DOAJ |
language |
English |
format |
Article |
sources |
DOAJ |
author |
Eleonora Sočo Dorota Papciak Magdalena M. Michel Dariusz Pająk Andżelika Domoń Bogdan Kupiec |
spellingShingle |
Eleonora Sočo Dorota Papciak Magdalena M. Michel Dariusz Pająk Andżelika Domoń Bogdan Kupiec Characterization of the Physical, Chemical, and Adsorption Properties of Coal-Fly-Ash–Hydroxyapatite Composites Minerals wet preparation method chemical engineering dye and heavy metals sorption industrial wastewater treatment |
author_facet |
Eleonora Sočo Dorota Papciak Magdalena M. Michel Dariusz Pająk Andżelika Domoń Bogdan Kupiec |
author_sort |
Eleonora Sočo |
title |
Characterization of the Physical, Chemical, and Adsorption Properties of Coal-Fly-Ash–Hydroxyapatite Composites |
title_short |
Characterization of the Physical, Chemical, and Adsorption Properties of Coal-Fly-Ash–Hydroxyapatite Composites |
title_full |
Characterization of the Physical, Chemical, and Adsorption Properties of Coal-Fly-Ash–Hydroxyapatite Composites |
title_fullStr |
Characterization of the Physical, Chemical, and Adsorption Properties of Coal-Fly-Ash–Hydroxyapatite Composites |
title_full_unstemmed |
Characterization of the Physical, Chemical, and Adsorption Properties of Coal-Fly-Ash–Hydroxyapatite Composites |
title_sort |
characterization of the physical, chemical, and adsorption properties of coal-fly-ash–hydroxyapatite composites |
publisher |
MDPI AG |
series |
Minerals |
issn |
2075-163X |
publishDate |
2021-07-01 |
description |
(1) Hydroxyapatite (HAp), which can be obtained by several methods, is known to be a good adsorbent. Coal fly ash (CFA) is a commonly reused byproduct also used in environmental applications as an adsorbent. We sought to answer the following question: Can CFA be included in the method of HAp wet synthesis to produce a composite capable of adsorbing both heavy metals and dyes? (2) High calcium lignite CFA from the thermal power plant in Bełchatów (Poland) was used as the base to prepare CFA–HAp composites. Four types designated CFA–HAp1–4 were synthesized via the wet method of in situ precipitation. The synthesis conditions differed in terms of the calcium reactants used, pH, and temperature. We also investigated the equilibrium adsorption of Cu(II) and rhodamine B (RB) on CFA–HAp1–4. The data were fitted using the Langmuir, Freundlich, and Redlich–Peterson models and validated using <i>R<sup>2</sup></i> and <i>χ</i><sup>2</sup>/<i>DoF</i>. Surface changes in CFA–HAp2 following Cu(II) and RB adsorption were assessed using SEM, SE, and FT-IR analysis. (3) The obtained composites contained hydroxyapatite (Ca/P 1.67) and aluminosilicates. The mode of Cu(II) and RB adsorption could be explained by the Redlich–Peterson model. The CFA–HAp2 obtained using CFA, Ca(NO<sub>3</sub>)<sub>2</sub>, and (NH<sub>4</sub>)<sub>2</sub>HPO<sub>4</sub> at RT and pH 11 exhibited the highest maximal adsorption capacity: 73.6 mg Cu/g and 87.0 mg RB/g. (4) The clear advantage of chemisorption over physisorption was indicated by the Cu(II)–CFA–HAp system. The RB molecules present in the form of uncharged lactone were favorably adsorbed even on strongly deprotonated CFA–HAp surfaces. |
topic |
wet preparation method chemical engineering dye and heavy metals sorption industrial wastewater treatment |
url |
https://www.mdpi.com/2075-163X/11/7/774 |
work_keys_str_mv |
AT eleonorasoco characterizationofthephysicalchemicalandadsorptionpropertiesofcoalflyashhydroxyapatitecomposites AT dorotapapciak characterizationofthephysicalchemicalandadsorptionpropertiesofcoalflyashhydroxyapatitecomposites AT magdalenammichel characterizationofthephysicalchemicalandadsorptionpropertiesofcoalflyashhydroxyapatitecomposites AT dariuszpajak characterizationofthephysicalchemicalandadsorptionpropertiesofcoalflyashhydroxyapatitecomposites AT andzelikadomon characterizationofthephysicalchemicalandadsorptionpropertiesofcoalflyashhydroxyapatitecomposites AT bogdankupiec characterizationofthephysicalchemicalandadsorptionpropertiesofcoalflyashhydroxyapatitecomposites |
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