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Alternative Method for the Treatment of Hydrometallurgical Arsenic–Calcium Residues: The Immobilization of Arsenic as Scorodite
Arsenic–calcium residue (ACR) is one of the major hazardous solid wastes produced by the metallurgical industry that poses a serious threat to the environment. However, a suitable method for the effective treatment of ACR is still lacking. In this study, an alternative treatment method for ACRs via...
Autores principales: | , , , , , , |
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Formato: | Online Artículo Texto |
Lenguaje: | English |
Publicado: |
American Chemical Society
2020
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Acceso en línea: | https://www.ncbi.nlm.nih.gov/pmc/articles/PMC7288567/ https://www.ncbi.nlm.nih.gov/pubmed/32548482 http://dx.doi.org/10.1021/acsomega.0c00849 |
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author | Ma, Xu Yuan, Zidan Zhang, Guoqing Zhang, Jiaxi Wang, Xin Wang, Shaofeng Jia, Yongfeng |
author_facet | Ma, Xu Yuan, Zidan Zhang, Guoqing Zhang, Jiaxi Wang, Xin Wang, Shaofeng Jia, Yongfeng |
author_sort | Ma, Xu |
collection | PubMed |
description | Arsenic–calcium residue (ACR) is one of the major hazardous solid wastes produced by the metallurgical industry that poses a serious threat to the environment. However, a suitable method for the effective treatment of ACR is still lacking. In this study, an alternative treatment method for ACRs via the immobilization of As as scorodite was proposed with the use of two types of ACRs (ACR(real) directly collected from a Pb refinery and ACR(lab) precipitated from waste sulfuric acid in the lab). The treatment of ACR included preparing the As-enriched solution via H(2)SO(4) dissolution–neutralization of ACR at pH < 2, As(III) was oxidized by H(2)O(2), and As(V) was immobilized as scorodite. The results showed that gypsum produced from ACR(lab) in the dissolution–neutralization process contained 68 mg/kg of As, far below the Chinese national standard for hazardous solid wastes (<0.1 wt %, GB5085.62007). The gypsum produced from ACR(real) contained 5400 mg/kg of As due to the presence of original high-As gypsum (1.6 wt %) in ACR(real). These results showed that the preliminary removal of SO(4)(2–) from waste sulfuric acid by lime neutralization–precipitation at pH ∼ 2 could produce pure-phase gypsum by avoiding the HAsO(4)(2–) isomorphic substitution for SO(4)(2–). The scorodite produced from both ACRs displayed good As stability at pH 4.95 (0.9 and 0.5 mg/L) via the toxicity characteristic leaching procedure (TCLP) method and at pH 3–7 (0.4–3.0 mg/L) via a 15 day short-term stability test. |
format | Online Article Text |
id | pubmed-7288567 |
institution | National Center for Biotechnology Information |
language | English |
publishDate | 2020 |
publisher | American Chemical Society |
record_format | MEDLINE/PubMed |
spelling | pubmed-72885672020-06-15 Alternative Method for the Treatment of Hydrometallurgical Arsenic–Calcium Residues: The Immobilization of Arsenic as Scorodite Ma, Xu Yuan, Zidan Zhang, Guoqing Zhang, Jiaxi Wang, Xin Wang, Shaofeng Jia, Yongfeng ACS Omega Arsenic–calcium residue (ACR) is one of the major hazardous solid wastes produced by the metallurgical industry that poses a serious threat to the environment. However, a suitable method for the effective treatment of ACR is still lacking. In this study, an alternative treatment method for ACRs via the immobilization of As as scorodite was proposed with the use of two types of ACRs (ACR(real) directly collected from a Pb refinery and ACR(lab) precipitated from waste sulfuric acid in the lab). The treatment of ACR included preparing the As-enriched solution via H(2)SO(4) dissolution–neutralization of ACR at pH < 2, As(III) was oxidized by H(2)O(2), and As(V) was immobilized as scorodite. The results showed that gypsum produced from ACR(lab) in the dissolution–neutralization process contained 68 mg/kg of As, far below the Chinese national standard for hazardous solid wastes (<0.1 wt %, GB5085.62007). The gypsum produced from ACR(real) contained 5400 mg/kg of As due to the presence of original high-As gypsum (1.6 wt %) in ACR(real). These results showed that the preliminary removal of SO(4)(2–) from waste sulfuric acid by lime neutralization–precipitation at pH ∼ 2 could produce pure-phase gypsum by avoiding the HAsO(4)(2–) isomorphic substitution for SO(4)(2–). The scorodite produced from both ACRs displayed good As stability at pH 4.95 (0.9 and 0.5 mg/L) via the toxicity characteristic leaching procedure (TCLP) method and at pH 3–7 (0.4–3.0 mg/L) via a 15 day short-term stability test. American Chemical Society 2020-05-28 /pmc/articles/PMC7288567/ /pubmed/32548482 http://dx.doi.org/10.1021/acsomega.0c00849 Text en Copyright © 2020 American Chemical Society This is an open access article published under an ACS AuthorChoice License (http://pubs.acs.org/page/policy/authorchoice_termsofuse.html) , which permits copying and redistribution of the article or any adaptations for non-commercial purposes. |
spellingShingle | Ma, Xu Yuan, Zidan Zhang, Guoqing Zhang, Jiaxi Wang, Xin Wang, Shaofeng Jia, Yongfeng Alternative Method for the Treatment of Hydrometallurgical Arsenic–Calcium Residues: The Immobilization of Arsenic as Scorodite |
title | Alternative Method for the Treatment of Hydrometallurgical
Arsenic–Calcium Residues: The Immobilization of Arsenic as
Scorodite |
title_full | Alternative Method for the Treatment of Hydrometallurgical
Arsenic–Calcium Residues: The Immobilization of Arsenic as
Scorodite |
title_fullStr | Alternative Method for the Treatment of Hydrometallurgical
Arsenic–Calcium Residues: The Immobilization of Arsenic as
Scorodite |
title_full_unstemmed | Alternative Method for the Treatment of Hydrometallurgical
Arsenic–Calcium Residues: The Immobilization of Arsenic as
Scorodite |
title_short | Alternative Method for the Treatment of Hydrometallurgical
Arsenic–Calcium Residues: The Immobilization of Arsenic as
Scorodite |
title_sort | alternative method for the treatment of hydrometallurgical
arsenic–calcium residues: the immobilization of arsenic as
scorodite |
url | https://www.ncbi.nlm.nih.gov/pmc/articles/PMC7288567/ https://www.ncbi.nlm.nih.gov/pubmed/32548482 http://dx.doi.org/10.1021/acsomega.0c00849 |
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