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Magnetic nanobiosorbent (MG‐Chi/Fe(3)O(4)) for dispersive solid‐phase extraction of Cu(II), Pb(II), and Cd(II) followed by flame atomic absorption spectrometry determination

Trace amounts of Cu (II), Pb (II), and Cd (II) in a wastewater sample were preconcentrated with a novel cross‐linked magnetic chitosan modified with a new synthesised methionine‐glutaraldehyde Schiff's base (MG‐Chi/Fe(3)O(4)) as a dispersive solid‐phase extraction (DSPE) adsorbent. The adsorbed...

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Autores principales: Salehi, Narges, Moghimi, Ali, Shahbazi, Hamidreza
Formato: Online Artículo Texto
Lenguaje:English
Publicado: John Wiley and Sons Inc. 2021
Materias:
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC8675810/
https://www.ncbi.nlm.nih.gov/pubmed/34694739
http://dx.doi.org/10.1049/nbt2.12025
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author Salehi, Narges
Moghimi, Ali
Shahbazi, Hamidreza
author_facet Salehi, Narges
Moghimi, Ali
Shahbazi, Hamidreza
author_sort Salehi, Narges
collection PubMed
description Trace amounts of Cu (II), Pb (II), and Cd (II) in a wastewater sample were preconcentrated with a novel cross‐linked magnetic chitosan modified with a new synthesised methionine‐glutaraldehyde Schiff's base (MG‐Chi/Fe(3)O(4)) as a dispersive solid‐phase extraction (DSPE) adsorbent. The adsorbed metal ions were then eluted with a specific volume of suitable solution and determined by flame atomic absorption spectrometry (FAAS). Various parameters affecting the extraction efficiency of the metal ions were investigated and optimised, including pH, amount of adsorbent, extraction time, type and volume rate of eluent, elution time, sample volume, and effect of interfering ions. The adsorption kinetics are more consistent with the pseudo‐second order model. The results were statistically interpreted and the analytical performance of the proposed method was found to have preconcentration factors of 55, 60, and 50 μg L(−1) for Cu(II), Pb(II), and Cd(II), respectively, limits of detection were 0.22, 0.24, and 0.10 μg L(−1) for Cu(II), Pb(II), and Cd(II), respectively, with a relative standard deviation (1.5%‐2.8 %), and the liner range was 5–1000 for Cu(II) and Pb(II) and 2.5–1000 for Cd(II). It was concluded that this method was suitable for successful simultaneous determination of Cu(II), Pb(II), and Cd(II) in industrial wastewater samples.
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spelling pubmed-86758102022-02-03 Magnetic nanobiosorbent (MG‐Chi/Fe(3)O(4)) for dispersive solid‐phase extraction of Cu(II), Pb(II), and Cd(II) followed by flame atomic absorption spectrometry determination Salehi, Narges Moghimi, Ali Shahbazi, Hamidreza IET Nanobiotechnol Original Research Papers Trace amounts of Cu (II), Pb (II), and Cd (II) in a wastewater sample were preconcentrated with a novel cross‐linked magnetic chitosan modified with a new synthesised methionine‐glutaraldehyde Schiff's base (MG‐Chi/Fe(3)O(4)) as a dispersive solid‐phase extraction (DSPE) adsorbent. The adsorbed metal ions were then eluted with a specific volume of suitable solution and determined by flame atomic absorption spectrometry (FAAS). Various parameters affecting the extraction efficiency of the metal ions were investigated and optimised, including pH, amount of adsorbent, extraction time, type and volume rate of eluent, elution time, sample volume, and effect of interfering ions. The adsorption kinetics are more consistent with the pseudo‐second order model. The results were statistically interpreted and the analytical performance of the proposed method was found to have preconcentration factors of 55, 60, and 50 μg L(−1) for Cu(II), Pb(II), and Cd(II), respectively, limits of detection were 0.22, 0.24, and 0.10 μg L(−1) for Cu(II), Pb(II), and Cd(II), respectively, with a relative standard deviation (1.5%‐2.8 %), and the liner range was 5–1000 for Cu(II) and Pb(II) and 2.5–1000 for Cd(II). It was concluded that this method was suitable for successful simultaneous determination of Cu(II), Pb(II), and Cd(II) in industrial wastewater samples. John Wiley and Sons Inc. 2021-02-19 /pmc/articles/PMC8675810/ /pubmed/34694739 http://dx.doi.org/10.1049/nbt2.12025 Text en © 2021 The Authors. IET Nanobiotechnology published by John Wiley & Sons Ltd on behalf of The Institution of Engineering and Technology. https://creativecommons.org/licenses/by/4.0/This is an open access article under the terms of the http://creativecommons.org/licenses/by/4.0/ (https://creativecommons.org/licenses/by/4.0/) License, which permits use, distribution and reproduction in any medium, provided the original work is properly cited.
spellingShingle Original Research Papers
Salehi, Narges
Moghimi, Ali
Shahbazi, Hamidreza
Magnetic nanobiosorbent (MG‐Chi/Fe(3)O(4)) for dispersive solid‐phase extraction of Cu(II), Pb(II), and Cd(II) followed by flame atomic absorption spectrometry determination
title Magnetic nanobiosorbent (MG‐Chi/Fe(3)O(4)) for dispersive solid‐phase extraction of Cu(II), Pb(II), and Cd(II) followed by flame atomic absorption spectrometry determination
title_full Magnetic nanobiosorbent (MG‐Chi/Fe(3)O(4)) for dispersive solid‐phase extraction of Cu(II), Pb(II), and Cd(II) followed by flame atomic absorption spectrometry determination
title_fullStr Magnetic nanobiosorbent (MG‐Chi/Fe(3)O(4)) for dispersive solid‐phase extraction of Cu(II), Pb(II), and Cd(II) followed by flame atomic absorption spectrometry determination
title_full_unstemmed Magnetic nanobiosorbent (MG‐Chi/Fe(3)O(4)) for dispersive solid‐phase extraction of Cu(II), Pb(II), and Cd(II) followed by flame atomic absorption spectrometry determination
title_short Magnetic nanobiosorbent (MG‐Chi/Fe(3)O(4)) for dispersive solid‐phase extraction of Cu(II), Pb(II), and Cd(II) followed by flame atomic absorption spectrometry determination
title_sort magnetic nanobiosorbent (mg‐chi/fe(3)o(4)) for dispersive solid‐phase extraction of cu(ii), pb(ii), and cd(ii) followed by flame atomic absorption spectrometry determination
topic Original Research Papers
url https://www.ncbi.nlm.nih.gov/pmc/articles/PMC8675810/
https://www.ncbi.nlm.nih.gov/pubmed/34694739
http://dx.doi.org/10.1049/nbt2.12025
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