Comparative Effect of UV, UV/H<sub>2</sub>O<sub>2</sub> and UV/H<sub>2</sub>O<sub>2</sub>/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...

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Main Authors: José Antonio Andrades, Manuel Lojo-López, Agata Egea-Corbacho, José María Quiroga
Format: Article
Language:English
Published: MDPI AG 2022-07-01
Series:Molecules
Subjects:
Online Access:https://www.mdpi.com/1420-3049/27/14/4507
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author José Antonio Andrades
Manuel Lojo-López
Agata Egea-Corbacho
José María Quiroga
author_facet José Antonio Andrades
Manuel Lojo-López
Agata Egea-Corbacho
José María Quiroga
author_sort José Antonio Andrades
collection DOAJ
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<sup>−1</sup> of H<sub>2</sub>O<sub>2</sub>. In semi-continuous reactors, the most efficient process was the photolysis of hydrogen peroxide with 2.5 mg L<sup>−1</sup> of H<sub>2</sub>O<sub>2</sub> 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.
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spelling doaj.art-7aa08c345db94a1188e533313781e9e22023-11-30T21:33:49ZengMDPI AGMolecules1420-30492022-07-012714450710.3390/molecules27144507Comparative Effect of UV, UV/H<sub>2</sub>O<sub>2</sub> and UV/H<sub>2</sub>O<sub>2</sub>/Fe on Terbuthylazine Degradation in Natural and Ultrapure WaterJosé Antonio Andrades0Manuel Lojo-López1Agata Egea-Corbacho2José María Quiroga3Department of Environmental Technologies, Faculty of Marine and Environmental Sciences, University of Cadiz, Puerto Real, 11510 Cadiz, SpainDepartment of Environmental Technologies, Faculty of Marine and Environmental Sciences, University of Cadiz, Puerto Real, 11510 Cadiz, SpainDepartment of Environmental Technologies, Faculty of Marine and Environmental Sciences, University of Cadiz, Puerto Real, 11510 Cadiz, SpainDepartment of Environmental Technologies, Faculty of Marine and Environmental Sciences, University of Cadiz, Puerto Real, 11510 Cadiz, SpainDifferent 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<sup>−1</sup> of H<sub>2</sub>O<sub>2</sub>. In semi-continuous reactors, the most efficient process was the photolysis of hydrogen peroxide with 2.5 mg L<sup>−1</sup> of H<sub>2</sub>O<sub>2</sub> 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.https://www.mdpi.com/1420-3049/27/14/4507advanced oxidation processes (AOPs)terbuthylazinenatural watersUV reactorsUPLC-MS
spellingShingle José Antonio Andrades
Manuel Lojo-López
Agata Egea-Corbacho
José María Quiroga
Comparative Effect of UV, UV/H<sub>2</sub>O<sub>2</sub> and UV/H<sub>2</sub>O<sub>2</sub>/Fe on Terbuthylazine Degradation in Natural and Ultrapure Water
Molecules
advanced oxidation processes (AOPs)
terbuthylazine
natural waters
UV reactors
UPLC-MS
title Comparative Effect of UV, UV/H<sub>2</sub>O<sub>2</sub> and UV/H<sub>2</sub>O<sub>2</sub>/Fe on Terbuthylazine Degradation in Natural and Ultrapure Water
title_full Comparative Effect of UV, UV/H<sub>2</sub>O<sub>2</sub> and UV/H<sub>2</sub>O<sub>2</sub>/Fe on Terbuthylazine Degradation in Natural and Ultrapure Water
title_fullStr Comparative Effect of UV, UV/H<sub>2</sub>O<sub>2</sub> and UV/H<sub>2</sub>O<sub>2</sub>/Fe on Terbuthylazine Degradation in Natural and Ultrapure Water
title_full_unstemmed Comparative Effect of UV, UV/H<sub>2</sub>O<sub>2</sub> and UV/H<sub>2</sub>O<sub>2</sub>/Fe on Terbuthylazine Degradation in Natural and Ultrapure Water
title_short Comparative Effect of UV, UV/H<sub>2</sub>O<sub>2</sub> and UV/H<sub>2</sub>O<sub>2</sub>/Fe on Terbuthylazine Degradation in Natural and Ultrapure Water
title_sort comparative effect of uv uv h sub 2 sub o sub 2 sub and uv h sub 2 sub o sub 2 sub fe on terbuthylazine degradation in natural and ultrapure water
topic advanced oxidation processes (AOPs)
terbuthylazine
natural waters
UV reactors
UPLC-MS
url https://www.mdpi.com/1420-3049/27/14/4507
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