Novel photocatalytic textile floater made with Ce0.85Y0.1Mg0.05O2-δ for the high degradation of methylene blue and fomesafen (Flex) under solar light

• Methylene-blue (MB) and fomesafen (FLEX) were degraded using a PETbased floater • CeO 2 :Y,Mg (CeYMgO) powder degraded MB/FLEX with 98-100% efficiency under sunlight • Composite floater T+G+CeYMgO degraded MB and FLEX with 90-98% under sunlight • The MB degradation efficiency of CeYMgO decreased 2% after three cycles of reuse • The predominant oxidizing species were (• O 2 − ), followed by (h+) and (•OH) In this work, photocatalytic floaters were made using polyethylene terephthalate (PET)-based textiles (T), graphene and CeO 2 :Y,Mg (CeYMgO) photocatalyst powder. This last material had a cubic structure and consisted in porous particles with an average size of 460 nm. Firstly, CeYMgO powder was evaluated for degradation of methylene-blue (MB) under solar light and it produced a maximum degradation of 95.65% (at pH=7) after 180 min under sunlight. Next, the textile was coated with graphene to form the T+G photocatalytic floater. Later, the T+G floater was coated with CeYMgO powder to make the T+G+CeYMgO photocatalytic floater. The T+G and T+G+CeYMgO floaters produced maximum MB degradation percentages of 93.16% and 98.2% (at pH=7), respectively, under sunlight. Fomesafen was also degraded at high percentage of 96% by the CeYMgO photocatalyst after 180 min under sunlight, but the initial pH of the contaminated water was low (pH=2.5). In addition, the T+G+CeYMgO floater degraded fomesafen but its efficiency was lower (90%) in comparison with the CeYMgO powder. The photocatalytic floater made with graphene+CeYMgO-powder had a higher content of defects (oxygen vacancies) than the T+G floater (as demonstrated by Raman and X-ray photoelectron spectroscopy (XPS) analyses). Therefore, it produced a higher degradation percentage for MB and fomesafen. Scavenger experiments were performed and found that the main oxidizing agents produced during the photocatalytic process are superoxide anions ( • O 2 − ), followed by holes (h+) and finally hydroxyl radicals (•OH). Furthermore, the T+G+CeYMgO photocatalytic floater induced the highest conversion from organic carbon to mineral carbon (77.98%), indicating that this floater produced the highest degradation of by-products. This investigation demonstrated that our photocatalytic floaters degraded contaminants due to the synergistic combination of porous CeYMgO, graphene with high absorption of sunlight and the entangled network of PET-based textile.

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Publication Details

Journal
Surfaces and Interfaces
Published
2025-05-15
DOI
https://doi.org/10.1016/j.surfin.2025.106711
Citations
4
Primary Topic
Advanced Photocatalysis Techniques
Type
article
Field-Weighted Citation Impact
1.45
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article

Novel photocatalytic textile floater made with Ce0.85Y0.1Mg0.05O2-δ for the high degradation of methylene blue and fomesafen (Flex) under solar light

J. Oliva, C.R. García, H. C. Rosu, José Manuel Díaz Moreno et al.
4 citations
Surfaces and Interfaces
Advanced Photocatalysis Techniques
1.45
article

Novel photocatalytic textile floater made with Ce0.85Y0.1Mg0.05O2-δ for the high degradation of methylene blue and fomesafen (Flex) under solar light

J. Oliva, C.R. García, H. C. Rosu, José Manuel Díaz Moreno, K.P. Padmasree, Tzipatly A. Esquivel‐Castro
article en
4 citations

Abstract

• Methylene-blue (MB) and fomesafen (FLEX) were degraded using a PETbased floater • CeO 2 :Y,Mg (CeYMgO) powder degraded MB/FLEX with 98-100% efficiency under sunlight • Composite floater T+G+CeYMgO degraded MB and FLEX with 90-98% under sunlight • The MB degradation efficiency of CeYMgO decreased 2% after three cycles of reuse • The predominant oxidizing species were (• O 2 − ), followed by (h+) and (•OH) In this work, photocatalytic floaters were made using polyethylene terephthalate (PET)-based textiles (T), graphene and CeO 2 :Y,Mg (CeYMgO) photocatalyst powder. This last material had a cubic structure and consisted in porous particles with an average size of 460 nm. Firstly, CeYMgO powder was evaluated for degradation of methylene-blue (MB) under solar light and it produced a maximum degradation of 95.65% (at pH=7) after 180 min under sunlight. Next, the textile was coated with graphene to form the T+G photocatalytic floater. Later, the T+G floater was coated with CeYMgO powder to make the T+G+CeYMgO photocatalytic floater. The T+G and T+G+CeYMgO floaters produced maximum MB degradation percentages of 93.16% and 98.2% (at pH=7), respectively, under sunlight. Fomesafen was also degraded at high percentage of 96% by the CeYMgO photocatalyst after 180 min under sunlight, but the initial pH of the contaminated water was low (pH=2.5). In addition, the T+G+CeYMgO floater degraded fomesafen but its efficiency was lower (90%) in comparison with the CeYMgO powder. The photocatalytic floater made with graphene+CeYMgO-powder had a higher content of defects (oxygen vacancies) than the T+G floater (as demonstrated by Raman and X-ray photoelectron spectroscopy (XPS) analyses). Therefore, it produced a higher degradation percentage for MB and fomesafen. Scavenger experiments were performed and found that the main oxidizing agents produced during the photocatalytic process are superoxide anions ( • O 2 − ), followed by holes (h+) and finally hydroxyl radicals (•OH). Furthermore, the T+G+CeYMgO photocatalytic floater induced the highest conversion from organic carbon to mineral carbon (77.98%), indicating that this floater produced the highest degradation of by-products. This investigation demonstrated that our photocatalytic floaters degraded contaminants due to the synergistic combination of porous CeYMgO, graphene with high absorption of sunlight and the entangled network of PET-based textile.

Surfaces and InterfacesVol. 68
Universidad Autónoma de Coahuila (MX), Institute for Scientific and Technological Research (MX), Centro de Investigación y de Estudios Avanzados del Instituto Politécnico Nacional (MX), Universidad Nacional Autónoma de México (MX)
Openalex Percentile: Top 19%
Advanced Photocatalysis Techniques
1.45
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