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Waste solidification/stabilization of lead–zinc slag by utilizing fly ash based geopolymers

Solidification/stabilization (S/S) is recognized as an effective technology for solid waste treatment. In S/S, the application of geopolymers synthesized by industrial waste (rich in active silicon and aluminum) to immobilize hazardous waste is a research focus. In this article, a fly ash based geop...

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Autores principales: Li, Shan, Huang, Xiao, Muhammad, Faheem, Yu, Lin, Xia, Ming, Zhao, Jian, Jiao, Binquan, Shiau, YanChyuan, Li, Dongwei
Formato: Online Artículo Texto
Lenguaje:English
Publicado: The Royal Society of Chemistry 2018
Materias:
Acceso en línea:https://www.ncbi.nlm.nih.gov/pmc/articles/PMC9086302/
https://www.ncbi.nlm.nih.gov/pubmed/35547705
http://dx.doi.org/10.1039/c8ra06634e
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author Li, Shan
Huang, Xiao
Muhammad, Faheem
Yu, Lin
Xia, Ming
Zhao, Jian
Jiao, Binquan
Shiau, YanChyuan
Li, Dongwei
author_facet Li, Shan
Huang, Xiao
Muhammad, Faheem
Yu, Lin
Xia, Ming
Zhao, Jian
Jiao, Binquan
Shiau, YanChyuan
Li, Dongwei
author_sort Li, Shan
collection PubMed
description Solidification/stabilization (S/S) is recognized as an effective technology for solid waste treatment. In S/S, the application of geopolymers synthesized by industrial waste (rich in active silicon and aluminum) to immobilize hazardous waste is a research focus. In this article, a fly ash based geopolymer was used to immobilize lead–zinc slag containing Pb, Ni, Zn and Mn. A fly ash based geopolymer with good mechanical strength was obtained through single factor experiments and the compressive strength of the geopolymer reached 29.72 MPa. The effects of immobilizing lead–zinc slag in the fly ash based geopolymer were discussed by means of compressive strength, leaching test and speciation analysis. The solidification/stabilization mechanism was further investigated using XRD, FTIR and SEM. The mechanical properties of the fly ash based geopolymer were negatively affected by addition of lead–zinc slag, and compressive strength decreased to 8.67 MPa when 60% lead–zinc slag was added. The geopolymer has the ability to reduce toxicity of lead–zinc slag by immobilizing heavy metals (Pb, Ni, Zn and Mn), but the ability was not unlimited. The migration of heavy metals to residual form indicates that heavy metals may either be bonded into the geopolymer matrix via the T–O bond (T = Si, Al) or captured in framework cavities to maintain the charge balance. The NASH (Na(2)O–Al(2)O(3)–SiO(2)–H(2)O) gel structure observed by XRD, FTIR and SEM can physically encapsulate the contaminants during geopolymerization. It is finally concluded that heavy metals were immobilized in the fly ash based geopolymer through a combination of chemical bonding and physical encapsulation.
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spelling pubmed-90863022022-05-10 Waste solidification/stabilization of lead–zinc slag by utilizing fly ash based geopolymers Li, Shan Huang, Xiao Muhammad, Faheem Yu, Lin Xia, Ming Zhao, Jian Jiao, Binquan Shiau, YanChyuan Li, Dongwei RSC Adv Chemistry Solidification/stabilization (S/S) is recognized as an effective technology for solid waste treatment. In S/S, the application of geopolymers synthesized by industrial waste (rich in active silicon and aluminum) to immobilize hazardous waste is a research focus. In this article, a fly ash based geopolymer was used to immobilize lead–zinc slag containing Pb, Ni, Zn and Mn. A fly ash based geopolymer with good mechanical strength was obtained through single factor experiments and the compressive strength of the geopolymer reached 29.72 MPa. The effects of immobilizing lead–zinc slag in the fly ash based geopolymer were discussed by means of compressive strength, leaching test and speciation analysis. The solidification/stabilization mechanism was further investigated using XRD, FTIR and SEM. The mechanical properties of the fly ash based geopolymer were negatively affected by addition of lead–zinc slag, and compressive strength decreased to 8.67 MPa when 60% lead–zinc slag was added. The geopolymer has the ability to reduce toxicity of lead–zinc slag by immobilizing heavy metals (Pb, Ni, Zn and Mn), but the ability was not unlimited. The migration of heavy metals to residual form indicates that heavy metals may either be bonded into the geopolymer matrix via the T–O bond (T = Si, Al) or captured in framework cavities to maintain the charge balance. The NASH (Na(2)O–Al(2)O(3)–SiO(2)–H(2)O) gel structure observed by XRD, FTIR and SEM can physically encapsulate the contaminants during geopolymerization. It is finally concluded that heavy metals were immobilized in the fly ash based geopolymer through a combination of chemical bonding and physical encapsulation. The Royal Society of Chemistry 2018-09-24 /pmc/articles/PMC9086302/ /pubmed/35547705 http://dx.doi.org/10.1039/c8ra06634e Text en This journal is © The Royal Society of Chemistry https://creativecommons.org/licenses/by-nc/3.0/
spellingShingle Chemistry
Li, Shan
Huang, Xiao
Muhammad, Faheem
Yu, Lin
Xia, Ming
Zhao, Jian
Jiao, Binquan
Shiau, YanChyuan
Li, Dongwei
Waste solidification/stabilization of lead–zinc slag by utilizing fly ash based geopolymers
title Waste solidification/stabilization of lead–zinc slag by utilizing fly ash based geopolymers
title_full Waste solidification/stabilization of lead–zinc slag by utilizing fly ash based geopolymers
title_fullStr Waste solidification/stabilization of lead–zinc slag by utilizing fly ash based geopolymers
title_full_unstemmed Waste solidification/stabilization of lead–zinc slag by utilizing fly ash based geopolymers
title_short Waste solidification/stabilization of lead–zinc slag by utilizing fly ash based geopolymers
title_sort waste solidification/stabilization of lead–zinc slag by utilizing fly ash based geopolymers
topic Chemistry
url https://www.ncbi.nlm.nih.gov/pmc/articles/PMC9086302/
https://www.ncbi.nlm.nih.gov/pubmed/35547705
http://dx.doi.org/10.1039/c8ra06634e
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