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Inhibition-based biosensor for cyanide detection – a preliminary study
INTRODUCTION: The acute toxicity of cyanide along with its continue industrial use makes this substance of environmental concern [1]. Titration, spectrophotometry and ISE are the standard detection methods. However, they are complex and need sample pre-treatment [2]. To overcome these, another appro...
Autores principales: | , , , |
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Formato: | Online Artículo Texto |
Lenguaje: | English |
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Taylor & Francis
2021
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Materias: | |
Acceso en línea: | https://www.ncbi.nlm.nih.gov/pmc/articles/PMC8480626/ http://dx.doi.org/10.1080/07853890.2021.1896915 |
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author | Coelho, Ana R. Monteiro, Tiago Viana, Ana S. Almeida, M. Gabriela |
author_facet | Coelho, Ana R. Monteiro, Tiago Viana, Ana S. Almeida, M. Gabriela |
author_sort | Coelho, Ana R. |
collection | PubMed |
description | INTRODUCTION: The acute toxicity of cyanide along with its continue industrial use makes this substance of environmental concern [1]. Titration, spectrophotometry and ISE are the standard detection methods. However, they are complex and need sample pre-treatment [2]. To overcome these, another approach is using biosensors. To this end, we developed a disposable inhibition-based biosensor with a multi-heme nitrite reductase (ccNiR) coupled to graphite leads. MATERIALS AND METHODS: Electrochemical measurements were carried out in a conventional electrochemical cell, composed by a three-electrode system. The reference was an Ag/AgCl electrode, and the counter electrode was a Pt wire. The working electrode (WE) was in-house made using a graphite lead with the ccNiR (from bacteria D. desulfuricans ATCC 27774; stored in 0.05 M phosphate buffer, pH 7.6) immobilised by drop cast at the WE surface. The electrochemical technique used was square wave voltammetry. Electrochemical cells contained 0.1 M KCl in 0.1 M Tris–HCl buffer (pH 7.6) as supporting electrolyte. Dissolved oxygen was removed by a biochemical system (GOx, catalase and glucose). DISCUSSION AND CONCLUSIONS: In Figure 1 we can observe the decrease in catalytic activity due to the presence of cyanide. The biosensor dynamic range comprises the maximum value imposed by the European Union, 1.92 µM (98/83/EC directive), which does not happen with other cyanide biosensors [3]. Furthermore, a graphite lead cost 0.35€ and each of them can be split, allowing a very low-cost biosensor. Given that enzyme inhibition is reversible [4], the sensor can be used more than one time, if we optimise the enzyme immobilisation method. |
format | Online Article Text |
id | pubmed-8480626 |
institution | National Center for Biotechnology Information |
language | English |
publishDate | 2021 |
publisher | Taylor & Francis |
record_format | MEDLINE/PubMed |
spelling | pubmed-84806262022-03-03 Inhibition-based biosensor for cyanide detection – a preliminary study Coelho, Ana R. Monteiro, Tiago Viana, Ana S. Almeida, M. Gabriela Ann Med Abstract 64 INTRODUCTION: The acute toxicity of cyanide along with its continue industrial use makes this substance of environmental concern [1]. Titration, spectrophotometry and ISE are the standard detection methods. However, they are complex and need sample pre-treatment [2]. To overcome these, another approach is using biosensors. To this end, we developed a disposable inhibition-based biosensor with a multi-heme nitrite reductase (ccNiR) coupled to graphite leads. MATERIALS AND METHODS: Electrochemical measurements were carried out in a conventional electrochemical cell, composed by a three-electrode system. The reference was an Ag/AgCl electrode, and the counter electrode was a Pt wire. The working electrode (WE) was in-house made using a graphite lead with the ccNiR (from bacteria D. desulfuricans ATCC 27774; stored in 0.05 M phosphate buffer, pH 7.6) immobilised by drop cast at the WE surface. The electrochemical technique used was square wave voltammetry. Electrochemical cells contained 0.1 M KCl in 0.1 M Tris–HCl buffer (pH 7.6) as supporting electrolyte. Dissolved oxygen was removed by a biochemical system (GOx, catalase and glucose). DISCUSSION AND CONCLUSIONS: In Figure 1 we can observe the decrease in catalytic activity due to the presence of cyanide. The biosensor dynamic range comprises the maximum value imposed by the European Union, 1.92 µM (98/83/EC directive), which does not happen with other cyanide biosensors [3]. Furthermore, a graphite lead cost 0.35€ and each of them can be split, allowing a very low-cost biosensor. Given that enzyme inhibition is reversible [4], the sensor can be used more than one time, if we optimise the enzyme immobilisation method. Taylor & Francis 2021-09-28 /pmc/articles/PMC8480626/ http://dx.doi.org/10.1080/07853890.2021.1896915 Text en © 2021 The Author(s). Published by Informa UK Limited, trading as Taylor & Francis Group https://creativecommons.org/licenses/by/4.0/This is an Open Access article distributed under the terms of the Creative Commons Attribution License (http://creativecommons.org/licenses/by/4.0/ (https://creativecommons.org/licenses/by/4.0/) ), which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited. |
spellingShingle | Abstract 64 Coelho, Ana R. Monteiro, Tiago Viana, Ana S. Almeida, M. Gabriela Inhibition-based biosensor for cyanide detection – a preliminary study |
title | Inhibition-based biosensor for cyanide detection – a preliminary study |
title_full | Inhibition-based biosensor for cyanide detection – a preliminary study |
title_fullStr | Inhibition-based biosensor for cyanide detection – a preliminary study |
title_full_unstemmed | Inhibition-based biosensor for cyanide detection – a preliminary study |
title_short | Inhibition-based biosensor for cyanide detection – a preliminary study |
title_sort | inhibition-based biosensor for cyanide detection – a preliminary study |
topic | Abstract 64 |
url | https://www.ncbi.nlm.nih.gov/pmc/articles/PMC8480626/ http://dx.doi.org/10.1080/07853890.2021.1896915 |
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