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Electro-Persulfate Processes for the Treatment of Complex Wastewater Matrices: Present and Future
Abstract
Complex wastewater matrices present a major environmental concern. Besides the biodegradable organics, they may contain a great variety of toxic chemicals, heavy metals, and other xenobiotics. The electrochemically activated persulfate process, an efficient way to generate sulfate radicals, has been widely applied to the degradation of such complex effluents with very good results. This review presents the fundamentals of the electro-persulfate processes, highlighting the advantages and limitations, followed by an exhaustive evaluation on the application of this process for the treatment of complex industrial effluents. An overview of the main relevant experimental parameters/details and their influence on the organic load removal is presented and discussed, having in mind the application of these technologies at an industrial scale. Finally, the future perspectives for the application of the electro-persulfate processes in the treatment of complex wastewater matrices is outlined.
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The practically unchanged sulfate concentration after EO is explained by reaction of reactive sulfate species with dissolved organic matter and by reactions that occur when no DOM is available for oxidation, which restore sulfate ions in the TDW.
“This is explained by the reaction of reactive sulfate species with dissolved organic matter (DOM) (Equation ( 8)) [35], and by reactions, such as that described in Equation (9), that occur when there is no DOM available for oxidation [33], which restore the sulfate ions in TDW.”
From Reuse of Textile Dyeing Wastewater Treated by Electrooxidation (2022) · cites this paper as [33]
Section 2 (Fundamentals of the Electro-Persulfate Processes; page unavailable) says sulfate radicals react with water and that persulfate regeneration after reactions with water or organics has been suggested. It does not say these reactions occur specifically when no DOM is available or that they explain an unchanged sulfate concentration in TDW. (LLM, conf=0.78)
Experimental — accuracy not yet measuredAccording to literature, sulfate radical is a strong and highly oxidizing species that presents higher redox potential than hydroxyl radicals or peroxodisulfate; it readily reacts at a wide range of pH values, promoting nonselective oxidation and efficient removal of a wide range of organic compounds [33].
“According to the literature, the sulfate radical is a strong and highly oxidizing species that presents higher redox potential than that of hydroxyl radicals or peroxodisulfate.It readily reacts at a wide range of pH values, promoting the nonselective oxidation and efficient removal of a wide range of organic compounds [33].”
From Reuse of Textile Dyeing Wastewater Treated by Electrooxidation (2022) · cites this paper as [33]
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Experimental — accuracy not yet measuredThe pH increase during EO can be attributed to cathode side reactions, to sulfate oxidation through hydroxyl radicals, and to formation of carbonates and bicarbonates from reaction of hydroxide ions with CO2 generated during oxidation of organic pollutants.
“This increase in pH during the EO process is well described in the literature and can be attributed to: (i) side reactions that occur at the cathode, such as the reaction described in Equation ( 7); (ii) sulfate oxidation through hydroxyl radicals (Equations ( 4) and ( 5)); and (iii) formation of carbonates and bicarbonates, from the reaction between the hydroxide ions and the CO 2 generated”
From Reuse of Textile Dyeing Wastewater Treated by Electrooxidation (2022) · cites this paper as [33]
Section 2 (Fundamentals of the Electro-Persulfate Processes; page unavailable) describes sulfate-ion oxidation by hydroxyl radicals, supporting one reaction named in the claim. The passages on pH in Sections 3.1 and 3.2 do not attribute an increase during electrooxidation to that reaction, cathode side reactions, or carbonate and bicarbonate formation from CO₂. (LLM, conf=0.76)
Experimental — accuracy not yet measuredMore recent studies on electro-persulfate processes show that when utilizing anode materials with high oxygen evolution potential, such as BDD, not only can peroxodisulfate be produced from oxidation of SO4 2-, but also sulfate radicals can be electrogenerated, either by sulfate ions direct oxidation or by oxidation through a hydroxyl radical [33].
“In fact, more recent studies on electro-persulfate processes show that, when utilizing anode materials with high oxygen evolution potential, such as BDD, not only can peroxodisulfate be produced from the oxidation of SO 4 2-(Equation ( 2)), but also sulfate radicals can be electrogenerated, either by sulfate ions direct oxidation (Equation ( 3)) or by oxidation through a hydroxyl radical (Equation”
From Reuse of Textile Dyeing Wastewater Treated by Electrooxidation (2022) · cites this paper as [33]
Peroxodisulfate can also be obtained through sulfate ions oxidation by hydroxyl radicals, and sulfate radicals can be generated from electrochemical activation of peroxodisulfate [33].
“Moreover, peroxodisulfate can be also obtained through sulfate ions oxidation by hydroxyl radicals (Equation ( 5)) and sulfate radicals can be generated from the electrochemical activation of peroxodisulfate, according to Equation (6) [33].”
From Reuse of Textile Dyeing Wastewater Treated by Electrooxidation (2022) · cites this paper as [33]
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“[8] 10 mA cm−2 100 1 20 mA cm−2 100 1 30 mA cm−2 100 1”
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Cited by
Sorted by citations
Reuse of Textile Dyeing Wastewater Treated by Electrooxidation
Pinto, C., Fernandes, A., Lopes, A., Nunes, M. J., Baía, A., Ciríaco, L., & Pacheco, M. J. (2022) · Water · doi:10.3390/w14071084 · Cited by 32
Self-citation
Metadata
- Authors
- Fernandes, A., Nunes, M. J., Rodrigues, A. S., Pacheco, M. J., Ciríaco, L., & Lopes, A.
- Venue
- Molecules
- Publisher
- MDPI AG
- Published
- 2021-08-09
- Volume
- 26
- Issue
- 16
- Pages
- 4821
- ISSN
- 1420-3049
- PMC
- PMC8401330
- Cited by
- 67
- References
- 2
- Language
- en
- Funders
- Fundação para a Ciência e a Tecnologia (Project UIDB/00195/2020, SFRH/BD/109901/2015, SFRH/BD/132436/2017)
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