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Novel Method for the Arsenic Removal Experiment and Mechanism Analysis

[Image: see text] This study focuses on the hydrothermal synthesis of magnetically activated carbon and its efficacy in As(III) adsorption. The successful incorporation of magnetite nanoparticles within the porous carbon structure was confirmed, enriching the adsorbent’s properties. Comprehensive ch...

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Autores principales: Zhu, Hao, Lin, Wenhui, Fan, Liwen
Formato: Online Artículo Texto
Lenguaje:English
Publicado: American Chemical Society 2023
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC10552136/
https://www.ncbi.nlm.nih.gov/pubmed/37810684
http://dx.doi.org/10.1021/acsomega.3c03590
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author Zhu, Hao
Lin, Wenhui
Fan, Liwen
author_facet Zhu, Hao
Lin, Wenhui
Fan, Liwen
author_sort Zhu, Hao
collection PubMed
description [Image: see text] This study focuses on the hydrothermal synthesis of magnetically activated carbon and its efficacy in As(III) adsorption. The successful incorporation of magnetite nanoparticles within the porous carbon structure was confirmed, enriching the adsorbent’s properties. Comprehensive characterization was performed to analyze the pore size distribution, zeta potential at varying pH levels, and thermostability using thermogravimetric analysis. These adsorbents exhibited high As(III) removal efficiency with a uniform pore distribution. The zeta potentials were observed to decrease with an increase in pH, suggesting a relationship between adsorbent charge and pH. Adsorption dynamics were rigorously modeled using pseudo-first-order, pseudo-second-order, Elovich, and intraparticle diffusion models for different adsorbents labeled as a,b,c, and d. Each adsorbent displayed unique fitted parameters, revealing varied adsorption capabilities. The study further explored the adsorption kinetics and found that the pseudo-second-order kinetics model and the Langmuir model were most appropriate for describing the adsorption process. Adsorption thermodynamics was also fitted to elucidate the underlying adsorption mechanisms. For the a,b,c, and d adsorbents, the pseudo-first-order model, the q(e)((cal)) values for the four adsorbents were 434.2, 418.4, 283.5, and 279.5 μg/g, respectively. Take adsorbent a as an example; the q(m) values for 298, 303, 308, and 313 K were 702, 673, 605, and 589 μg/g, respectively, and K(L) values of these temperatures were 0.021, 0.031, 0.018, and 0.009 L/μg, respectively. For the Langmuir model, the R(2) values at the four temperatures were 0.999, 0.978, 0.985, and 0.993, respectively, which indicated that the Langmuir model showed higher fitness. For the Freundlich model, the K(L) values (L/μg) at the parameters of these temperatures are 432, 409, 328, and 294, respectively. For the Freundlich model, the 1/n values at temperatures of 298, 303, 308, and 313 K are 0.049, 0.045, 0.052, and 0.035, respectively. For the Freundlich model, the R(2) values at parameters of 298, 303, 308, and 313 K are 0.986, 0.989, 0.982, and 0.872, respectively. For the Temkin model, the B values (in J/mol) are 30.93, 0.894, 0.824, and 0.782 at these temperatures, respectively. The K(T) values (in L/μg) are 1.02 × 10(6), 0.07 × 10(6), 0.003 × 10(6), and 0.002 × 10(6), respectively. The R(2) values are 0.973, 0.958, 0.972, and 0.894, respectively. In the end, the ΔH, ΔS, and ΔG values for different adsorbents were calculated. Collectively, these findings contribute significant insights into the design and application of magnetically activated carbon adsorbents for effective As(III) removal.
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spelling pubmed-105521362023-10-06 Novel Method for the Arsenic Removal Experiment and Mechanism Analysis Zhu, Hao Lin, Wenhui Fan, Liwen ACS Omega [Image: see text] This study focuses on the hydrothermal synthesis of magnetically activated carbon and its efficacy in As(III) adsorption. The successful incorporation of magnetite nanoparticles within the porous carbon structure was confirmed, enriching the adsorbent’s properties. Comprehensive characterization was performed to analyze the pore size distribution, zeta potential at varying pH levels, and thermostability using thermogravimetric analysis. These adsorbents exhibited high As(III) removal efficiency with a uniform pore distribution. The zeta potentials were observed to decrease with an increase in pH, suggesting a relationship between adsorbent charge and pH. Adsorption dynamics were rigorously modeled using pseudo-first-order, pseudo-second-order, Elovich, and intraparticle diffusion models for different adsorbents labeled as a,b,c, and d. Each adsorbent displayed unique fitted parameters, revealing varied adsorption capabilities. The study further explored the adsorption kinetics and found that the pseudo-second-order kinetics model and the Langmuir model were most appropriate for describing the adsorption process. Adsorption thermodynamics was also fitted to elucidate the underlying adsorption mechanisms. For the a,b,c, and d adsorbents, the pseudo-first-order model, the q(e)((cal)) values for the four adsorbents were 434.2, 418.4, 283.5, and 279.5 μg/g, respectively. Take adsorbent a as an example; the q(m) values for 298, 303, 308, and 313 K were 702, 673, 605, and 589 μg/g, respectively, and K(L) values of these temperatures were 0.021, 0.031, 0.018, and 0.009 L/μg, respectively. For the Langmuir model, the R(2) values at the four temperatures were 0.999, 0.978, 0.985, and 0.993, respectively, which indicated that the Langmuir model showed higher fitness. For the Freundlich model, the K(L) values (L/μg) at the parameters of these temperatures are 432, 409, 328, and 294, respectively. For the Freundlich model, the 1/n values at temperatures of 298, 303, 308, and 313 K are 0.049, 0.045, 0.052, and 0.035, respectively. For the Freundlich model, the R(2) values at parameters of 298, 303, 308, and 313 K are 0.986, 0.989, 0.982, and 0.872, respectively. For the Temkin model, the B values (in J/mol) are 30.93, 0.894, 0.824, and 0.782 at these temperatures, respectively. The K(T) values (in L/μg) are 1.02 × 10(6), 0.07 × 10(6), 0.003 × 10(6), and 0.002 × 10(6), respectively. The R(2) values are 0.973, 0.958, 0.972, and 0.894, respectively. In the end, the ΔH, ΔS, and ΔG values for different adsorbents were calculated. Collectively, these findings contribute significant insights into the design and application of magnetically activated carbon adsorbents for effective As(III) removal. American Chemical Society 2023-09-22 /pmc/articles/PMC10552136/ /pubmed/37810684 http://dx.doi.org/10.1021/acsomega.3c03590 Text en © 2023 The Authors. Published by American Chemical Society https://creativecommons.org/licenses/by-nc-nd/4.0/Permits non-commercial access and re-use, provided that author attribution and integrity are maintained; but does not permit creation of adaptations or other derivative works (https://creativecommons.org/licenses/by-nc-nd/4.0/).
spellingShingle Zhu, Hao
Lin, Wenhui
Fan, Liwen
Novel Method for the Arsenic Removal Experiment and Mechanism Analysis
title Novel Method for the Arsenic Removal Experiment and Mechanism Analysis
title_full Novel Method for the Arsenic Removal Experiment and Mechanism Analysis
title_fullStr Novel Method for the Arsenic Removal Experiment and Mechanism Analysis
title_full_unstemmed Novel Method for the Arsenic Removal Experiment and Mechanism Analysis
title_short Novel Method for the Arsenic Removal Experiment and Mechanism Analysis
title_sort novel method for the arsenic removal experiment and mechanism analysis
url https://www.ncbi.nlm.nih.gov/pmc/articles/PMC10552136/
https://www.ncbi.nlm.nih.gov/pubmed/37810684
http://dx.doi.org/10.1021/acsomega.3c03590
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