2018
DOI: 10.1007/s10098-018-1528-0
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Effect of Mn substitution on the oxidation/adsorption abilities of iron(III) oxyhydroxides

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Cited by 7 publications
(2 citation statements)
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“…In this last case, the kinetic model showed constants of k 2 = 0.1866 (g mg −1 min −1 ) and q e = 0.425 (mg g −1 ). On the other hand, smaller k 2 values, below 0.01 mg g −1 min −1 , were shown by Yang et al [40] in the adsorption of As(III) by ZnO microtubes; and also in adsorption experiments at similar initial concentrations of Mn@FeO x composites [41]. It is worth noting that for all of these cases, the results of this study with CTO showed higher qe even at pH 7.…”
Section: Resultscontrasting
confidence: 46%
“…In this last case, the kinetic model showed constants of k 2 = 0.1866 (g mg −1 min −1 ) and q e = 0.425 (mg g −1 ). On the other hand, smaller k 2 values, below 0.01 mg g −1 min −1 , were shown by Yang et al [40] in the adsorption of As(III) by ZnO microtubes; and also in adsorption experiments at similar initial concentrations of Mn@FeO x composites [41]. It is worth noting that for all of these cases, the results of this study with CTO showed higher qe even at pH 7.…”
Section: Resultscontrasting
confidence: 46%
“…Although arsenite is more toxic and prevalent in groundwater, it has less affinity towards adsorbent surface due to its non-ionic nature, whereas arsenate exists as ionic species in the pH range of 4-10 which makes it easily removable. In general, for arsenite removal, pre-oxidation is involved which converts arsenite into arsenate, then it gets removed from the aqueous solution (Cho et al, 2018). Therefore, for the present study, only arsenate removal has been considered.…”
Section: Introductionmentioning
confidence: 99%