2017
DOI: 10.1002/jctb.5209
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Adsorptive performance of nanosized zero‐valent iron for V(V) removal from aqueous solutions

Abstract: BACKGROUND Vanadium is included in the USEPA Contaminant Candidate List. It is an essential dietary mineral but it becomes toxic at high concentrations causing health problems. In this study, nanosized zero‐valent iron (nZVI) was synthesized and the applicability of the sorbent was investigated for the removal of V(V) in water samples. RESULTS The synthesized sorbent is characterized by scanning electron microscopy‐energy dispersive X‐ray spectroscopy, thermo gravimetric and Brunauer–Emmett–Teller surface area… Show more

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Cited by 37 publications
(14 citation statements)
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“…This suggests that on the surface, vanadium was bound by surface hydroxyl groups without a change in oxidation state change. A similar result was reported for the vanadium adsorption onto nanosized zero-valent iron [43]. It was proposed that vanadium(V) ions were bound to the outer shell of the iron sorbent via surface complexation [43].…”
Section: Dissolution Of Fe-gwtr and Characterization Of Fe-gwtr Solutionsupporting
confidence: 80%
See 1 more Smart Citation
“…This suggests that on the surface, vanadium was bound by surface hydroxyl groups without a change in oxidation state change. A similar result was reported for the vanadium adsorption onto nanosized zero-valent iron [43]. It was proposed that vanadium(V) ions were bound to the outer shell of the iron sorbent via surface complexation [43].…”
Section: Dissolution Of Fe-gwtr and Characterization Of Fe-gwtr Solutionsupporting
confidence: 80%
“…A similar result was reported for the vanadium adsorption onto nanosized zero-valent iron [43]. It was proposed that vanadium(V) ions were bound to the outer shell of the iron sorbent via surface complexation [43]. The surface physical parameters of raw peat and Fe-GWTR-P3 are shown in Table 3.…”
Section: Dissolution Of Fe-gwtr and Characterization Of Fe-gwtr Solutionsupporting
confidence: 77%
“…The amount of Pb(II) adsorbed, q (mg g −1 ), was calculated using Equation (1). [ 26 ] The influence of adsorption parameters viz., pH (2–8), contact time (5–180 min), sorbent amount (2.5–30.0 mg) and temperature (298–343 K) were examined, and the optimum adsorption conditions were determined q=CnormaliCnormaleV/Wwhere W (g) is the weight of sorbent in the solution, C i and C e (mg L −1 ) are initial and equilibrium concentrations of Pb(II) ions and V (L) is the volume of the solution.…”
Section: Methodsmentioning
confidence: 99%
“…Moreover, K F is the Freundlich's constant (mg g −1 ) and n F is a dimensionless number in this model (Equation (3)). [ 26 ] The D – R isotherm model assumes that the ionic species preferentially bind to most energetically favorable sites of sorbent associated with multilayer adsorption of ions. The D – R isotherm model is generally described by Equations (4–6).…”
Section: Methodsmentioning
confidence: 99%
“…The mean free energy E (kJ mol -1 ) of sorption can be estimated by using β values as expressed in the following Eqn. 5 -7 [16,17] ( 5 )…”
Section: Dubinin-radushkevich (D-r) Modelmentioning
confidence: 99%