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dc.contributor.authorPardina Aizpitarte, Diego
dc.contributor.authorSantamaría, Asier
dc.contributor.authorAlonso Alonso, María Luz ORCID
dc.contributor.authorBartolomé Moro, Luis Javier
dc.contributor.authorAlonso Rojas, Rosa María ORCID
dc.contributor.authorMaña Iglesias, Jon Ander
dc.contributor.authorBilbao, Elisabeth
dc.contributor.authorLombraña Alonso, José Ignacio ORCID
dc.contributor.authorBartolomé, Mikel
dc.contributor.authorHernando, Luis M.
dc.date.accessioned2023-02-28T15:36:09Z
dc.date.available2023-02-28T15:36:09Z
dc.date.issued2023-01-21
dc.identifier.citationChemosensors 11(2) : (2023) // Article ID 84es_ES
dc.identifier.issn2227-9040
dc.identifier.urihttp://hdl.handle.net/10810/60176
dc.description.abstractDrinking water treatment plants (DWTP) use chlorination as an oxidation stage in the first step of the processes used to eliminate the natural organic matter (NOM) responsible for the formation of 2-methylisoborneol (2-MIB) and Geosmin (GM), which produce odor and taste to the water. However, chlorination processes give rise to disinfectant toxic subproducts, such as trihalomethanes (THMs). In this work, a headspace solid-phase microextraction coupled with a gas chromatography/mass spectrometric method has been developed for the quality control of drinking water. 2-MIB, GM, and THMs at different stages of the drinking water treatment process were monitored. The method was validated following the Environmental Protection Agency guidelines. Neither carryover nor the matrix effect was observed. The performance of the method was satisfactory in terms of selectivity, repeatability, and accuracy and exhibited a linear concentration range of 0.8–50 µg/L for trichloromethane (TCM), 0.05–20 µg/L for bromodichloromethane, 0.01–20 µg/L for dibromochloromethane and tribromomethane, and 0.005–0.05 µg/L for GM and 2-MIB. The THMs concentration obtained for all the water samples was below the thresholds established by international organizations and, for 2-MIB and GM, were lower for their limit of quantification. The method was also applied to the adsorption kinetic study of TCM on granulated activated carbon, which is the main barrier to reducing the NOM in DWTP.es_ES
dc.description.sponsorshipThis research was funded by Consorcio de Aguas Bilbao Bizkaia, grant number OTRI: 2019.0756 (project CETHAP) and the APC was funded by the University of Basque Country.es_ES
dc.language.isoenges_ES
dc.publisherMDPIes_ES
dc.rightsinfo:eu-repo/semantics/openAccesses_ES
dc.rights.urihttp://creativecommons.org/licenses/by/4.0/
dc.subjecttrihalomethaneses_ES
dc.subjectgeosmines_ES
dc.subject2-methylisoborneoles_ES
dc.subjectsolid-phase microextractiones_ES
dc.subjectgas chromatographyes_ES
dc.subjectmass spectrometryes_ES
dc.titleHS-SPME-GC/MS Method for the Simultaneous Determination of Trihalomethanes, Geosmin, and 2-Methylisoborneol in Water Sampleses_ES
dc.typeinfo:eu-repo/semantics/articlees_ES
dc.date.updated2023-02-24T14:08:14Z
dc.rights.holder© 2023 by the authors. 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/).es_ES
dc.relation.publisherversionhttps://www.mdpi.com/2227-9040/11/2/84es_ES
dc.identifier.doi10.3390/chemosensors11020084
dc.departamentoesIngeniería química
dc.departamentoesQuímica analítica
dc.departamentoeuIngeniaritza kimikoa
dc.departamentoeuKimika analitikoa


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© 2023 by the authors. 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/).
Except where otherwise noted, this item's license is described as © 2023 by the authors. 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/).