2021
DOI: 10.1016/j.cej.2021.130812
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Fabrication of cellulose@Mg(OH)2 composite filter via interfacial bonding and its trapping effect for heavy metal ions

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Cited by 29 publications
(6 citation statements)
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“…All the samples showed the similar general patterns seen in Figure 1 a. The diffraction peak located at 2θ of 20.0° is the characteristic peak of polyvinyl alcohol (PVA), and the peak appearing at 22.7° belongs to the (002) diffraction plane of cellulose [ 44 ]. The diffraction peaks at 31.8°, 34.4° and 36.…”
Section: Resultsmentioning
confidence: 95%
“…All the samples showed the similar general patterns seen in Figure 1 a. The diffraction peak located at 2θ of 20.0° is the characteristic peak of polyvinyl alcohol (PVA), and the peak appearing at 22.7° belongs to the (002) diffraction plane of cellulose [ 44 ]. The diffraction peaks at 31.8°, 34.4° and 36.…”
Section: Resultsmentioning
confidence: 95%
“…The adsorption kinetics were described using the pseudo-first-order and pseudo-second-order models, corresponding to eqs and , respectively. The adsorption isotherm was usually expressed with the Langmuir or Freundlich model, having eqs and , respectively. q e = c 0 c t m × V Here, q e (mg·g –1 ) denotes the adsorption capacity in equilibrium, c 0 and c t are the initial and final concentrations (mg·L –1 ), respectively, and m (g) and V (L) represent the mass of the adsorbent and the volume of the solution, respectively. q t = q e ( 1 e k 1 t ) t q t = 1 k 2 q e 2 + t q normale Here, q t (mg·g –1 ) and q e (mg·g –1 ) are the adsorption amount versus time t (min) and at equilibrium; k 1 (min –1 ) and k 2 (g·mg –1 ·min –1 ) represent the rate constants of the pseudo-first-order and pseudo-second-order models, respectively. c normale q normale = 1 K L q max + c normale q max ln nobreak0em0.25em⁡ q e = ln nobreak0em0.25em⁡ K F + 1 n…”
Section: Methodsmentioning
confidence: 99%
“…The adsorption isotherm was usually expressed with the Langmuir or Freundlich model, having eqs 4 and 5 , respectively. 42 45 Here, q e (mg·g –1 ) denotes the adsorption capacity in equilibrium, c 0 and c t are the initial and final concentrations (mg·L –1 ), respectively, and m (g) and V (L) represent the mass of the adsorbent and the volume of the solution, respectively. Here, q t (mg·g –1 ) and q e (mg·g –1 ) are the adsorption amount versus time t (min) and at equilibrium; k 1 (min –1 ) and k 2 (g·mg –1 ·min –1 ) represent the rate constants of the pseudo-first-order and pseudo-second-order models, respectively.…”
Section: Methodsmentioning
confidence: 99%
“…Modified or composite magnesium hydroxide has been widely used to remove heavy metals from water. Zhao [20] prepared a cellulose@Mg(OH) 2 composite film with excellent heavy metal removal. Rachid [21] synthesized a novel chitosanloaded MgAl-LDH nanocomposite, and its performance in As(V) removal and antimicrobial activity was evaluated.…”
Section: Introductionmentioning
confidence: 99%