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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...

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Autores principales: Coelho, Ana R., Monteiro, Tiago, Viana, Ana S., Almeida, M. Gabriela
Formato: Online Artículo Texto
Lenguaje:English
Publicado: Taylor & Francis 2021
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.
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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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