Re-recognizing micro locations of nanoscale zero-valent iron in biochar using C-TEM technique

Abstract Biochar supported nanoscale zero-valent iron (NZVI/BC), prepared commonly by liquid reduction using sodium borohydride (NaBH4), exhibits better reduction performance for contaminants than bare NZVI. The better reducing ability was attributed to attachment of nanoscale zero-valent iron (NZVI...

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Main Authors: Kun Yang, Jialu Xu, Ming Zhang, Daohui Lin
Format: Article
Language:English
Published: Nature Publishing Group 2021-03-01
Series:Scientific Reports
Online Access:https://doi.org/10.1038/s41598-021-84685-w
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spelling doaj-b9f6600254d54449a03d64763335540d2021-03-11T12:19:27ZengNature Publishing GroupScientific Reports2045-23222021-03-0111111010.1038/s41598-021-84685-wRe-recognizing micro locations of nanoscale zero-valent iron in biochar using C-TEM techniqueKun Yang0Jialu Xu1Ming Zhang2Daohui Lin3Department of Environmental Science, Zhejiang UniversityDepartment of Environmental Science, Zhejiang UniversityDepartment of Environmental Engineering, China Jiliang UniversityDepartment of Environmental Science, Zhejiang UniversityAbstract Biochar supported nanoscale zero-valent iron (NZVI/BC), prepared commonly by liquid reduction using sodium borohydride (NaBH4), exhibits better reduction performance for contaminants than bare NZVI. The better reducing ability was attributed to attachment of nanoscale zero-valent iron (NZVI) on biochar (BC) surface or into the interior pores of BC particles due to observations by scanning electron microscopy (SEM) and plan transmission electron microscopy (P-TEM) techniques in previous studies. In this study, cross-sectional TEM (C-TEM) technique was employed firstly to explore location of NZVI in NZVI/BC. It was observed that NZVI is isolated from BC particles, but not located on the surface or in the interior pores of BC particles. This observation was also supported by negligible adsorption and precipitation of Fe2+/Fe3+ and iron hydroxides on BC surface or into interior pores of BC particles respectively. Precipitation of Fe2+ and Fe3+, rather than adsorption, is responsible for the removal of Fe2+ and Fe3+ by BC. Moreover, precipitates of iron hydroxides cannot be reduced to NZVI by NaBH4. In addition to SEM or P-TEM, therefore, C-TEM is a potential technique to characterize the interior morphology of NZVI/BC for better understanding the improved reduction performance of contaminants by NZVI/BC than bare NZVI.https://doi.org/10.1038/s41598-021-84685-w
collection DOAJ
language English
format Article
sources DOAJ
author Kun Yang
Jialu Xu
Ming Zhang
Daohui Lin
spellingShingle Kun Yang
Jialu Xu
Ming Zhang
Daohui Lin
Re-recognizing micro locations of nanoscale zero-valent iron in biochar using C-TEM technique
Scientific Reports
author_facet Kun Yang
Jialu Xu
Ming Zhang
Daohui Lin
author_sort Kun Yang
title Re-recognizing micro locations of nanoscale zero-valent iron in biochar using C-TEM technique
title_short Re-recognizing micro locations of nanoscale zero-valent iron in biochar using C-TEM technique
title_full Re-recognizing micro locations of nanoscale zero-valent iron in biochar using C-TEM technique
title_fullStr Re-recognizing micro locations of nanoscale zero-valent iron in biochar using C-TEM technique
title_full_unstemmed Re-recognizing micro locations of nanoscale zero-valent iron in biochar using C-TEM technique
title_sort re-recognizing micro locations of nanoscale zero-valent iron in biochar using c-tem technique
publisher Nature Publishing Group
series Scientific Reports
issn 2045-2322
publishDate 2021-03-01
description Abstract Biochar supported nanoscale zero-valent iron (NZVI/BC), prepared commonly by liquid reduction using sodium borohydride (NaBH4), exhibits better reduction performance for contaminants than bare NZVI. The better reducing ability was attributed to attachment of nanoscale zero-valent iron (NZVI) on biochar (BC) surface or into the interior pores of BC particles due to observations by scanning electron microscopy (SEM) and plan transmission electron microscopy (P-TEM) techniques in previous studies. In this study, cross-sectional TEM (C-TEM) technique was employed firstly to explore location of NZVI in NZVI/BC. It was observed that NZVI is isolated from BC particles, but not located on the surface or in the interior pores of BC particles. This observation was also supported by negligible adsorption and precipitation of Fe2+/Fe3+ and iron hydroxides on BC surface or into interior pores of BC particles respectively. Precipitation of Fe2+ and Fe3+, rather than adsorption, is responsible for the removal of Fe2+ and Fe3+ by BC. Moreover, precipitates of iron hydroxides cannot be reduced to NZVI by NaBH4. In addition to SEM or P-TEM, therefore, C-TEM is a potential technique to characterize the interior morphology of NZVI/BC for better understanding the improved reduction performance of contaminants by NZVI/BC than bare NZVI.
url https://doi.org/10.1038/s41598-021-84685-w
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AT mingzhang rerecognizingmicrolocationsofnanoscalezerovalentironinbiocharusingctemtechnique
AT daohuilin rerecognizingmicrolocationsofnanoscalezerovalentironinbiocharusingctemtechnique
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