Better Together Than Apart: Degradation of Emerging Contaminants in Concentrated Streams Using UV/Sulfite/Iodide and UV/Hydrogen Peroxide Treatment Trains

High Resolution Image Download MS PowerPoint Slide This study evaluates the performance of homogeneous UV-based advanced reduction processes (ARPs) and advanced oxidation processes (AOPs), applied individually and in sequential treatment trains as a largely unexplored approach for the degradation of aqueous contaminants. UVC/SO 3 2– and UVC/SO 3 2– /I – were the reference ARPs, while UVC/H 2 O 2 was used as the reference AOP. A mixture of three model contaminants was used in all cases, consisting of perfluorooctanoic acid (PFOA, as a model perfluoroalkyl substance─PFAS), ibuprofen, and benzoic acid. The UVC/SO 3 2– treatment achieved 70% defluorination of 100 μM PFOA after 24 h of irradiation, while nearly complete defluorination was obtained with UVC/SO 3 2– /I – in the same period. Benzoic acid exhibited the fastest degradation rates with both ARPs ( k obs = 3.9 × 10 –1 min –1, 100 μM concentration), whereas ibuprofen was considerably slower, being comparable to its direct photolysis ( k obs = 2.9 × 10 –2 min –1, 100 μM concentration). In contrast, the UVC/H 2 O 2 process efficiently mineralized benzoic acid and ibuprofen (>99% within 2 h) but showed negligible degradation of PFOA (<1% in 2 h). The treatment trains (AOP → ARP and ARP → AOP) were decisively more efficient when dealing with the pollutant mixture degradation in the presence of scavengers. With the AOP → ARP approach, for matrices containing 50 mg L –1 of humic acids, the UVC/H 2 O 2 pretreatment led to faster PFOA defluorination rates than ARPs alone (65% and 5% in 2 h, respectively). The inverse configuration, ARP → AOP, allowed the mineralization of PFOA, a result that could not be achieved when either ARPs or the AOP were applied individually. Experiments in simulated retentate wastewater, containing 1 μM of each contaminant and high concentration of anions and organic matter, were consistent with the preliminary results. This work is one of the first to offer valuable information on the degradation of PFAS and non-PFAS pollutants by the aforementioned treatment trains, especially in concentrated wastewater treatment streams.

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Publication Details

Journal
ACS Environmental Au
Published
2026-07-01
DOI
https://doi.org/10.1021/acsenvironau.6c00098
Primary Topic
Advanced oxidation water treatment
Type
article
Field-Weighted Citation Impact
0.00

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article

Better Together Than Apart: Degradation of Emerging Contaminants in Concentrated Streams Using UV/Sulfite/Iodide and UV/Hydrogen Peroxide Treatment Trains

Ana Agüera, Patricia Plaza‐Bolaños, Iván Sciscenko, Claudio Minero et al.
ACS Environmental Au
Advanced oxidation water treatment
article

Better Together Than Apart: Degradation of Emerging Contaminants in Concentrated Streams Using UV/Sulfite/Iodide and UV/Hydrogen Peroxide Treatment Trains

Ana Agüera, Patricia Plaza‐Bolaños, Iván Sciscenko, Claudio Minero, Marco Minella, Agustín París-Reche
article en

Abstract

High Resolution Image Download MS PowerPoint Slide This study evaluates the performance of homogeneous UV-based advanced reduction processes (ARPs) and advanced oxidation processes (AOPs), applied individually and in sequential treatment trains as a largely unexplored approach for the degradation of aqueous contaminants. UVC/SO 3 2– and UVC/SO 3 2– /I – were the reference ARPs, while UVC/H 2 O 2 was used as the reference AOP. A mixture of three model contaminants was used in all cases, consisting of perfluorooctanoic acid (PFOA, as a model perfluoroalkyl substance─PFAS), ibuprofen, and benzoic acid. The UVC/SO 3 2– treatment achieved 70% defluorination of 100 μM PFOA after 24 h of irradiation, while nearly complete defluorination was obtained with UVC/SO 3 2– /I – in the same period. Benzoic acid exhibited the fastest degradation rates with both ARPs ( k obs = 3.9 × 10 –1 min –1, 100 μM concentration), whereas ibuprofen was considerably slower, being comparable to its direct photolysis ( k obs = 2.9 × 10 –2 min –1, 100 μM concentration). In contrast, the UVC/H 2 O 2 process efficiently mineralized benzoic acid and ibuprofen (>99% within 2 h) but showed negligible degradation of PFOA (<1% in 2 h). The treatment trains (AOP → ARP and ARP → AOP) were decisively more efficient when dealing with the pollutant mixture degradation in the presence of scavengers. With the AOP → ARP approach, for matrices containing 50 mg L –1 of humic acids, the UVC/H 2 O 2 pretreatment led to faster PFOA defluorination rates than ARPs alone (65% and 5% in 2 h, respectively). The inverse configuration, ARP → AOP, allowed the mineralization of PFOA, a result that could not be achieved when either ARPs or the AOP were applied individually. Experiments in simulated retentate wastewater, containing 1 μM of each contaminant and high concentration of anions and organic matter, were consistent with the preliminary results. This work is one of the first to offer valuable information on the degradation of PFAS and non-PFAS pollutants by the aforementioned treatment trains, especially in concentrated wastewater treatment streams.

ACS Environmental Au
University of Almería (ES), University of Turin (IT)
Dipartimenti di Eccellenza, HORIZON EUROPE Framework Programme, Agencia Estatal de Investigación, H2020 Marie Skłodowska-Curie Actions
Clean water and sanitation
Openalex Percentile: Top 14%
Advanced oxidation water treatment
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