2020
DOI: 10.1021/acs.iecr.0c04347
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Trace Cr(VI) Removal: Evidence of Redox-Active Ion Exchange by a Weak-Base Anion Exchanger

Abstract: The presence of Cr(VI) in water, even in trace concentrations, is toxic to numerous animals, plants, and microorganisms. Remediation efforts require selective removal of trace concentrations of Cr(VI) anions from the background of other competing ions present in concentrations at least 2 orders of magnitude greater than Cr(VI). The objective of this study was to evaluate the trace Cr(VI) removal capacities of commonly available anion exchangers. Batch and column studies revealed that Duolite A7 showed extraord… Show more

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Cited by 20 publications
(9 citation statements)
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“…The Q e Cr /(IEC/2) value slightly exceeded unity in some iCONs (e.g., 122% for II, 107% for VI, and 110% for VII) possibly due to the concurring non-ion-exchange adsorption pathways. 32,59 The pore size appeared to have some impact on the Cr uptake efficiency as iCON I with the smallest pore size showed a slightly lower Q e Cr /(IEC/2) value of 80%. Interestingly, the Q e Cr /(IEC/2) values were comparable between iCONs with syn-(III) and anti-hydrogen bonding conformations (II) at the guanidinium sites, suggesting that the parallel bidentate hydrogen bonding interactions with tetrahedral oxoanion are not essential to chromate adsorption.…”
Section: ■ Results and Discussionmentioning
confidence: 99%
“…The Q e Cr /(IEC/2) value slightly exceeded unity in some iCONs (e.g., 122% for II, 107% for VI, and 110% for VII) possibly due to the concurring non-ion-exchange adsorption pathways. 32,59 The pore size appeared to have some impact on the Cr uptake efficiency as iCON I with the smallest pore size showed a slightly lower Q e Cr /(IEC/2) value of 80%. Interestingly, the Q e Cr /(IEC/2) values were comparable between iCONs with syn-(III) and anti-hydrogen bonding conformations (II) at the guanidinium sites, suggesting that the parallel bidentate hydrogen bonding interactions with tetrahedral oxoanion are not essential to chromate adsorption.…”
Section: ■ Results and Discussionmentioning
confidence: 99%
“…It is worth mentioning that the Cr(VI)/Cr(III) redox process also occurred, though to a much smaller extent, in iCON-OH 0 presumably due to the presence of unreacted amine and aldehyde groups. [10,22] Further analysis with iCON-OH 1-2 revealed that the Q m /(IEC/2) values in chromate adsorption linearly increase with the number of hydroxyl groups on the aromatic linker (Figure 3e), indicating a phenol-mediated redox conversion. [11] The phenol-mediated Cr(VI)/Cr(III) redox process in iCON-OH 3 as well as in iCON-OH 1-2 was clearly accelerated by the ion exchange process as the control neutral hydroxylated CON-OH 0-3 showed insignificant redox-based adsorption of chromate at the neutral pH (Figure 3f).…”
Section: Adsorption Of Chromate and Arsenate In Mono-oxoanion Environmentsmentioning
confidence: 99%
“…[ 1 ] Organic dyes (such as Congo Red [CR] and Methyl orange [MO]) are widely used in the textile industry, and the dye pollutants can induce water quality deterioration and adversely affect human health. [ 2 ] Nowadays, the standard methods for wastewater treatment include adsorption, [ 3 ] photocatalysis reduction, [ 4 ] membrane separation, [ 5,6 ] ion exchange, [ 7 ] and electrochemical methods [ 1 ] that have been used to remove pollutants from wastewater. [ 8 ] Among them, adsorption is regarded as the most promising method because of its low pollution and economic performance.…”
Section: Introductionmentioning
confidence: 99%