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Predicting Cu and Zn sorption capacity of biochar from feedstock C/N ratio and pyrolysis temperature
Biochars have been proposed for remediation of metal-contaminated water due to their low cost, high surface area and high sorption capacity for metals. However, there is a lack of understanding over how feedstock material and pyrolysis conditions contribute to the metal sorption capacity of biochar....
Autores principales: | , , , , , |
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Formato: | Online Artículo Texto |
Lenguaje: | English |
Publicado: |
Springer Berlin Heidelberg
2017
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Materias: | |
Acceso en línea: | https://www.ncbi.nlm.nih.gov/pmc/articles/PMC5847629/ https://www.ncbi.nlm.nih.gov/pubmed/29288302 http://dx.doi.org/10.1007/s11356-017-1047-2 |
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author | Rodríguez-Vila, Alfonso Selwyn-Smith, Heather Enunwa, Laurretta Smail, Isla Covelo, Emma F. Sizmur, Tom |
author_facet | Rodríguez-Vila, Alfonso Selwyn-Smith, Heather Enunwa, Laurretta Smail, Isla Covelo, Emma F. Sizmur, Tom |
author_sort | Rodríguez-Vila, Alfonso |
collection | PubMed |
description | Biochars have been proposed for remediation of metal-contaminated water due to their low cost, high surface area and high sorption capacity for metals. However, there is a lack of understanding over how feedstock material and pyrolysis conditions contribute to the metal sorption capacity of biochar. We produced biochars from 10 different organic materials by pyrolysing at 450 °C and a further 10 biochars from cedar wood by pyrolysing at 50 °C intervals (250–700 °C). Batch sorption experiments were conducted to derive the maximum Cu and Zn sorption capacity of each biochar. The results revealed an exponential relationship between Cu and Zn sorption capacity and the feedstock C/N ratio and a sigmoidal relationship between the pyrolysis temperature and the maximum Cu and Zn sorption capacity. FTIR analysis revealed that as temperature increased, the abundance of functional groups reduced. We conclude that the high sorption capacity of high temperature biochars is due to an electrostatic attraction between positively charged Cu and Zn ions and delocalised pi-electrons on the greater surface area of these biochars. These findings demonstrate a method for predicting the maximum sorption capacity of a biochar based on the feedstock C/N ratio and the pyrolysis temperature. ELECTRONIC SUPPLEMENTARY MATERIAL: The online version of this article (10.1007/s11356-017-1047-2) contains supplementary material, which is available to authorized users. |
format | Online Article Text |
id | pubmed-5847629 |
institution | National Center for Biotechnology Information |
language | English |
publishDate | 2017 |
publisher | Springer Berlin Heidelberg |
record_format | MEDLINE/PubMed |
spelling | pubmed-58476292018-03-20 Predicting Cu and Zn sorption capacity of biochar from feedstock C/N ratio and pyrolysis temperature Rodríguez-Vila, Alfonso Selwyn-Smith, Heather Enunwa, Laurretta Smail, Isla Covelo, Emma F. Sizmur, Tom Environ Sci Pollut Res Int Research Article Biochars have been proposed for remediation of metal-contaminated water due to their low cost, high surface area and high sorption capacity for metals. However, there is a lack of understanding over how feedstock material and pyrolysis conditions contribute to the metal sorption capacity of biochar. We produced biochars from 10 different organic materials by pyrolysing at 450 °C and a further 10 biochars from cedar wood by pyrolysing at 50 °C intervals (250–700 °C). Batch sorption experiments were conducted to derive the maximum Cu and Zn sorption capacity of each biochar. The results revealed an exponential relationship between Cu and Zn sorption capacity and the feedstock C/N ratio and a sigmoidal relationship between the pyrolysis temperature and the maximum Cu and Zn sorption capacity. FTIR analysis revealed that as temperature increased, the abundance of functional groups reduced. We conclude that the high sorption capacity of high temperature biochars is due to an electrostatic attraction between positively charged Cu and Zn ions and delocalised pi-electrons on the greater surface area of these biochars. These findings demonstrate a method for predicting the maximum sorption capacity of a biochar based on the feedstock C/N ratio and the pyrolysis temperature. ELECTRONIC SUPPLEMENTARY MATERIAL: The online version of this article (10.1007/s11356-017-1047-2) contains supplementary material, which is available to authorized users. Springer Berlin Heidelberg 2017-12-29 2018 /pmc/articles/PMC5847629/ /pubmed/29288302 http://dx.doi.org/10.1007/s11356-017-1047-2 Text en © The Author(s) 2017 Open Access This article is distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution, and reproduction in any medium, provided you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made. |
spellingShingle | Research Article Rodríguez-Vila, Alfonso Selwyn-Smith, Heather Enunwa, Laurretta Smail, Isla Covelo, Emma F. Sizmur, Tom Predicting Cu and Zn sorption capacity of biochar from feedstock C/N ratio and pyrolysis temperature |
title | Predicting Cu and Zn sorption capacity of biochar from feedstock C/N ratio and pyrolysis temperature |
title_full | Predicting Cu and Zn sorption capacity of biochar from feedstock C/N ratio and pyrolysis temperature |
title_fullStr | Predicting Cu and Zn sorption capacity of biochar from feedstock C/N ratio and pyrolysis temperature |
title_full_unstemmed | Predicting Cu and Zn sorption capacity of biochar from feedstock C/N ratio and pyrolysis temperature |
title_short | Predicting Cu and Zn sorption capacity of biochar from feedstock C/N ratio and pyrolysis temperature |
title_sort | predicting cu and zn sorption capacity of biochar from feedstock c/n ratio and pyrolysis temperature |
topic | Research Article |
url | https://www.ncbi.nlm.nih.gov/pmc/articles/PMC5847629/ https://www.ncbi.nlm.nih.gov/pubmed/29288302 http://dx.doi.org/10.1007/s11356-017-1047-2 |
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