2020
DOI: 10.1002/jeq2.20144
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Identifying the mechanisms of cation inhibition of phenol oxidation by acid birnessite

Abstract: Many phenolic compounds found as contaminants in natural waters are susceptible to oxidation by manganese oxides. However, there is often variability between oxidation rates reported in pristine matrices and studies using more environmentally relevant conditions. For example, the presence of cations generally results in slower phenolic oxidation rates. However, the underlying mechanism of cation interference is not well understood. In this study, cation co-solutes inhibit the transformation of four target phen… Show more

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Cited by 6 publications
(10 citation statements)
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“…In contrast, initial E 2 :E 3 values only significantly correlate with percent changes in E 2 :E 3 ( p = 0.047), indicating that apparent molecular weight of DOM is not a major predictor of its reactivity. Furthermore, although sulfate and ionic strength may influence the reactivity of manganese oxides , and DOM, ,,,,, they are not correlated with measured parameters in these samples.…”
Section: Resultsmentioning
confidence: 81%
“…In contrast, initial E 2 :E 3 values only significantly correlate with percent changes in E 2 :E 3 ( p = 0.047), indicating that apparent molecular weight of DOM is not a major predictor of its reactivity. Furthermore, although sulfate and ionic strength may influence the reactivity of manganese oxides , and DOM, ,,,,, they are not correlated with measured parameters in these samples.…”
Section: Resultsmentioning
confidence: 81%
“…Taking into account that oxidation is most likely preceded by sorption of I – on the surface so that electron transfer can take place, electrostatic repulsion may hinder the interaction. δ-MnO 2 is a mineral with different pH pzc values between its edge sites and vacancy sites, 6–8 and 2–3, respectively . This would give δ-MnO 2 both localized positive and negative sites in different regions of the mineral, allowing I – to be capable of sorbing at edge sites, but perhaps not on the vacancy site, which would lead to a moderate level of I – oxidation (Figure a).…”
Section: Resultsmentioning
confidence: 99%
“…δ-MnO 2 is a mineral with different pH pzc values between its edge sites and vacancy sites, 6−8 and 2−3, respectively. 38 This would give δ-MnO 2 both localized positive and negative sites in different regions of the mineral, allowing I − to be capable of sorbing at edge sites, but perhaps not on the vacancy site, which would lead to a moderate level of I − oxidation (Figure 1a). This is consistent with electron transfer between birnessite and anions occurring exclusively on the edge sites.…”
Section: ■ Experimental Sectionmentioning
confidence: 99%
“…Anions were not considered due to repulsive electrostatic interactions between the negatively charged acid birnessite and anions. 26,28,85,86 Kinetic reactions using a nonspecific radical quencher tertbutanol 87−91 were conducted to explore the role of radicalmediated reactions in enhancing the rate of bisphenol A oxidation using water samples from DL1, DL2, and WW1. tert-Butanol (50 mM) was used as it is not likely to react with manganese oxides and does not alter the mineral surface.…”
Section: ■ Materials and Methodsmentioning
confidence: 99%
“…13,26−28 This trend is attributable to the stronger sorption of divalent cations to manganese oxide surfaces compared to that of monovalent cations. 13,26,31 Furthermore, divalent cations can interact with other organic compounds in solution, such as dissolved organic matter (DOM), to form complexes or increase DOM sorption to mineral surfaces (Figure S1). 32 DOM is a mixture of organic molecules found in natural and engineered systems 38−43 and can also impact phenolic compound oxidation by manganese oxides.…”
Section: ■ Introductionmentioning
confidence: 99%