2021
DOI: 10.1016/j.envres.2021.111431
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Removal of arsenic from aqueous solution by novel iron and iron–zirconium modified activated carbon derived from chemical carbonization of Tectona grandis sawdust: Isotherm, kinetic, thermodynamic and breakthrough curve modelling

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Cited by 42 publications
(17 citation statements)
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“…Due to the addition of metal oxides and hydroxyl groups on the surface of the material and the increase in active sites, the adsorption capacity of ZIC to Sb( v ) is greatly improved compared with unmodified activated carbon. 12 When the molar ratios of iron to zirconium ions in the ZIC were 1 : 1, 1 : 3 and 1 : 5, the removal rates of Sb( v ) were 77.11%, 61.49% and 56.4%, respectively. The surface of zirconia has a special pore structure, which is favourable to the diffusion of Sb( v ) in the pores.…”
Section: Resultsmentioning
confidence: 96%
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“…Due to the addition of metal oxides and hydroxyl groups on the surface of the material and the increase in active sites, the adsorption capacity of ZIC to Sb( v ) is greatly improved compared with unmodified activated carbon. 12 When the molar ratios of iron to zirconium ions in the ZIC were 1 : 1, 1 : 3 and 1 : 5, the removal rates of Sb( v ) were 77.11%, 61.49% and 56.4%, respectively. The surface of zirconia has a special pore structure, which is favourable to the diffusion of Sb( v ) in the pores.…”
Section: Resultsmentioning
confidence: 96%
“…This shows that the nanoparticles are successfully loaded on the surface of the activated carbon and distributed evenly, which reduces the reunion phenomenon. 12 Moreover, some particles enter the pores of activated carbon, which has stronger adhesion and does not easily fall off, which makes the ZIC nanocomposite material stable.…”
Section: Resultsmentioning
confidence: 99%
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“…A piece of NCMs of known weight (≈1 g) was immersed in 50 mL of the arsenic solution under stirring for 6 h. Afterward, the final arsenic concentration was quantified, and the adsorption capacity in each point calculated considering the weight of the nanocomposite membrane was calculated considering the nanocomposite membrane weight. The isotherm curves were fitted to the following models: Langmuir, [ 57 ] Freundlich, [ 58 ] Temkin, [ 59 ] Dubinin–Radushkevich, [ 60 ] and Halsey, [ 61 ] which were defined by Equations ()–(), respectively qnormale = QmaxbCnormale1 + bCnormale qnormale = KnormalFCnormale1/n qnormale = RTbTlnKTCe qnormale = QnormalSexpBnormalDε2 ε = RTln1 + 1Cnormale qnormale = KnormalHCnormale1/n where q e (mg g −1 ) is the As adsorption capacity at a given equilibrium concentration, C e (mg L −1 ) is the arsenic equilibrium...…”
Section: Methodsmentioning
confidence: 99%
“… 12 19 Among these options, adsorption is one of the efficient techniques for the removal of As from contaminated water as this technique is simple, cost-effective, and produces less waste products. 20 22 Various adsorbents such as clay, modified clay, and clay supported nano zero valent iron (nZVI), 23 26 alumina, 27 29 activated carbon, 30 32 graphene, 33 and biochar (BC) 34 36 have been used to remove As from contaminated waters.…”
Section: Introductionmentioning
confidence: 99%