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Comparative Effect of UV, UV/H(2)O(2) and UV/H(2)O(2)/Fe on Terbuthylazine Degradation in Natural and Ultrapure Water
Different advanced oxidation processes (AOPs) (ultraviolet radiation, hydrogen peroxide photolysis and photo-Fenton) were applied to test the degradation of terbuthylazine in three types of water: (a) ultrapure water, (b) surface water from the Gaditana area (Los Hurones reservoir, Cádiz, Spain) and...
Autores principales: | , , , |
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Formato: | Online Artículo Texto |
Lenguaje: | English |
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MDPI
2022
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Materias: | |
Acceso en línea: | https://www.ncbi.nlm.nih.gov/pmc/articles/PMC9321380/ https://www.ncbi.nlm.nih.gov/pubmed/35889384 http://dx.doi.org/10.3390/molecules27144507 |
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author | Andrades, José Antonio Lojo-López, Manuel Egea-Corbacho, Agata Quiroga, José María |
author_facet | Andrades, José Antonio Lojo-López, Manuel Egea-Corbacho, Agata Quiroga, José María |
author_sort | Andrades, José Antonio |
collection | PubMed |
description | Different advanced oxidation processes (AOPs) (ultraviolet radiation, hydrogen peroxide photolysis and photo-Fenton) were applied to test the degradation of terbuthylazine in three types of water: (a) ultrapure water, (b) surface water from the Gaditana area (Los Hurones reservoir, Cádiz, Spain) and (c) groundwater from the Tempul spring in Jerez de la Frontera (Cádiz, Spain). The experiments were carried out on a laboratory scale, using two different types of reactors, batch and semi-continuous. In batch reactors, the most efficient process for the experiments carried out with both ultrapure water and underground groundwater was ultraviolet radiation, whereas for surface water from the Gaditana area, the process that obtained the best results was the photolysis of hydrogen peroxide with 2.5 mg L(−1) of H(2)O(2). In semi-continuous reactors, the most efficient process was the photolysis of hydrogen peroxide with 2.5 mg L(−1) of H(2)O(2) for all the matrices studied. In both types of reactors, terbuthylazine degradation percentages higher than 90% were achieved; the main difference was in the reaction time, which varied from minutes in the batch reactor to seconds in the semi-continuous reactor. In all the applied AOPs, N-terbutyl-6-hydroxy-N′ethyl-1,3,5-triazine-2,4-diamine (TBA-212) was generated as a reaction intermediate. |
format | Online Article Text |
id | pubmed-9321380 |
institution | National Center for Biotechnology Information |
language | English |
publishDate | 2022 |
publisher | MDPI |
record_format | MEDLINE/PubMed |
spelling | pubmed-93213802022-07-27 Comparative Effect of UV, UV/H(2)O(2) and UV/H(2)O(2)/Fe on Terbuthylazine Degradation in Natural and Ultrapure Water Andrades, José Antonio Lojo-López, Manuel Egea-Corbacho, Agata Quiroga, José María Molecules Article Different advanced oxidation processes (AOPs) (ultraviolet radiation, hydrogen peroxide photolysis and photo-Fenton) were applied to test the degradation of terbuthylazine in three types of water: (a) ultrapure water, (b) surface water from the Gaditana area (Los Hurones reservoir, Cádiz, Spain) and (c) groundwater from the Tempul spring in Jerez de la Frontera (Cádiz, Spain). The experiments were carried out on a laboratory scale, using two different types of reactors, batch and semi-continuous. In batch reactors, the most efficient process for the experiments carried out with both ultrapure water and underground groundwater was ultraviolet radiation, whereas for surface water from the Gaditana area, the process that obtained the best results was the photolysis of hydrogen peroxide with 2.5 mg L(−1) of H(2)O(2). In semi-continuous reactors, the most efficient process was the photolysis of hydrogen peroxide with 2.5 mg L(−1) of H(2)O(2) for all the matrices studied. In both types of reactors, terbuthylazine degradation percentages higher than 90% were achieved; the main difference was in the reaction time, which varied from minutes in the batch reactor to seconds in the semi-continuous reactor. In all the applied AOPs, N-terbutyl-6-hydroxy-N′ethyl-1,3,5-triazine-2,4-diamine (TBA-212) was generated as a reaction intermediate. MDPI 2022-07-14 /pmc/articles/PMC9321380/ /pubmed/35889384 http://dx.doi.org/10.3390/molecules27144507 Text en © 2022 by the authors. https://creativecommons.org/licenses/by/4.0/Licensee MDPI, Basel, Switzerland. This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (https://creativecommons.org/licenses/by/4.0/). |
spellingShingle | Article Andrades, José Antonio Lojo-López, Manuel Egea-Corbacho, Agata Quiroga, José María Comparative Effect of UV, UV/H(2)O(2) and UV/H(2)O(2)/Fe on Terbuthylazine Degradation in Natural and Ultrapure Water |
title | Comparative Effect of UV, UV/H(2)O(2) and UV/H(2)O(2)/Fe on Terbuthylazine Degradation in Natural and Ultrapure Water |
title_full | Comparative Effect of UV, UV/H(2)O(2) and UV/H(2)O(2)/Fe on Terbuthylazine Degradation in Natural and Ultrapure Water |
title_fullStr | Comparative Effect of UV, UV/H(2)O(2) and UV/H(2)O(2)/Fe on Terbuthylazine Degradation in Natural and Ultrapure Water |
title_full_unstemmed | Comparative Effect of UV, UV/H(2)O(2) and UV/H(2)O(2)/Fe on Terbuthylazine Degradation in Natural and Ultrapure Water |
title_short | Comparative Effect of UV, UV/H(2)O(2) and UV/H(2)O(2)/Fe on Terbuthylazine Degradation in Natural and Ultrapure Water |
title_sort | comparative effect of uv, uv/h(2)o(2) and uv/h(2)o(2)/fe on terbuthylazine degradation in natural and ultrapure water |
topic | Article |
url | https://www.ncbi.nlm.nih.gov/pmc/articles/PMC9321380/ https://www.ncbi.nlm.nih.gov/pubmed/35889384 http://dx.doi.org/10.3390/molecules27144507 |
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