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Review of kinetics of chemical and photocatalytical oxidation of Arsenic(III) as influenced by pH
Abstract
The kinetics and stoichiometry of As(III) oxidation by chemical oxidants is presented. The reactions are first-order with respect to each reactant. The second-order rate constants vary with pH and have a range in magnitude of 10(4)-10(7) M-1 s-1 for free available chlorine (FAC), O3, and FeO4(2-) in a pH range of 6.0-9.0. In this pH range, the reactions of As(III) with chloroamine (NH2Cl) and H2O2 are quite slow with rate constants of 2.9-4.3x10(-1) M-1 s-1 and 2.6x10(-2)-4.5x10(1) M-1 s-1 for chloroamine and H2O2, respectively. The pH dependence of the oxidation reactions can be described using acid-base equilibria of both As(III) species and the oxidant. FAC, O3, and FeO(4)2- oxidize As(III) instantaneously at pH 7.0 with half-lives of milliseconds if 2 mg/L excess dose of oxidant is applied. One major advantage of FeO4(2-) ions over the other oxidants is its ability to remove arsenic in water by two mechanisms; it oxidizes As(III) and also subsequently coagulates As(V) through Fe(III) hydroxide produced from Fe(VI) reduction. Photocatalytic oxidation of As(III) to As(V) follows zero-order kinetics and the oxidation is completed in minutes with no significant pH dependence. The removal of dissolved arsenic to values below the World Health Organization drinking water limit of 10 microg/L can be achieved through photocatalytic oxidation of As(III) to As(V) in acidic solution followed by adsorption of As(V) onto TiO2 surfaces.
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“The reaction is very fast for permanganate, chlorine, and ozone as compared to hydrogen peroxide and chloramine when applied for oxidation of AsIII to AsV [142–144].”
From Arsenic Contamination of Groundwater: A Review of Sources, Prevalence, Health Risks, and Strategies for Mitigation (2014) · cites this paper as [143]
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Cited by
Sorted by citations
Shankar, S., Shanker, U., & Shikha (2014) · The Scientific World Journal · doi:10.1155/2014/304524 · Cited by 616
“UV/solar light facilitates the generation of hydroxyl radicals through the photolysis of Fe(III) species (FeOH 2 ) and in presence of both hydroxyl radicals and O 2 , the rate of oxidation becomes faster [147, 148].”
BackgroundIron and aluminium based adsorption strategies for removing arsenic from water
Giles, D. E., Mohapatra, M., Issa, T. B., Anand, S., & Singh, P. (2011) · Journal of Environmental Management · doi:10.1016/j.jenvman.2011.07.018 · Cited by 345
Metadata
- Authors
- Sharma, V. K., Dutta, P. K., & Ray, A. K.
- Affiliations
- Florida Institute of Technology (US)
- The University of Queensland (AU)
- Western University (CA)
- Venue
- Journal of Environmental Science and Health, Part A
- Publisher
- Informa UK Limited
- Published
- 2007-05-31
- Volume
- 42
- Issue
- 7
- Pages
- 997-1004
- ISSN
- 1093-4529 (ISSN-L)
- 1532-4117
- OpenAlex
- W2062786133
- Cited by
- 88
- References
- 2
- Citations by year
- 2026: 1 · 2025: 2 · 2024: 10 · 2023: 3 · 2022: 3 · 2021: 8 · 2020: 6 · 2019: 9 · 2018: 5 · 2017: 2 · 2016: 5 · 2015: 1 · 2014: 9 · 2013: 5 · 2012: 3
- FWCI
- 2.63
- Type
- journal article
- Language
- en
- Open access
- closed
- Locations
- Journal of Environmental Science and Health Part A (publishedVersion)
- PubMed (publishedVersion)
- Topics
- Physical Sciences › Environmental Science › Environmental Chemistry › Arsenic contamination and mitigation
- Physical Sciences › Environmental Science › Health, Toxicology and Mutagenesis › Water Treatment and Disinfection
- Physical Sciences › Environmental Science › Water Science and Technology › Advanced oxidation water treatment
- Keywords
- arsenic(III) oxidation, arsenic removal, oxidation kinetics, pH dependence, photocatalytic oxidation, permanganate, ozone, free chlorine, chloramines, hydrogen peroxide, acid-base balance, adsorption on TiO2, drinking water treatment
- MeSH terms
- Arsenic, Catalysis, Chloramines, Hydrogen Peroxide, Hydrogen-Ion Concentration, Kinetics, Oxidation-Reduction, Photochemistry, Water Supply, Water Purification, Iron Compounds
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