2022
DOI: 10.1016/j.scitotenv.2021.151258
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Synthesis of graphene oxide/polyethyleneimine sponge and its performance in the sustainable removal of Cu(II) from water

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Cited by 32 publications
(20 citation statements)
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“…These activated function groups consider as available negative active site that can form a complex with the cationic pollutants. In order to improve the adsorption efficiency of GO, numerous studies were investigated to liable GO in another constructures such as; graphene oxide (GO), sodium alginate (SA) and hydroxyethyl cellulose (HEC) (SA-HEC/GO bio-adsorbent hydrogel beads 8 , graphene oxide/hollow mesoporous silica (GO–HMS) composite 9 , sodium alginate/gelatin/graphene oxide (SGGO) nanocomposite 10 , polyaniline/graphene oxide (PANI/GO) nanocomposite 11 , graphene oxide-chitosan-EDTA (GO–EDTA–CS) nanocomposite 12 , polyethyleneimine (PEI) modified (GO) to form (GO/PEI) sponge 13 , decoration of GO with zinc oxide nanoparticles (ZnO) (GO/ZnO) 14 , graphene oxide (GO) modified with isocyanate (MDI), subsequently, (EDTA) (EDTA/MDI/GO) composite 15 , modification of graphene oxide (GO) nanosheets with magnetic particles of nickel ferrite (NiFe 2 O 4 ) and followed by immobilizing glutathione (GSH) to fabrication of GSH-NiFe 2 O 4 /GO nanocomposite 16 and Amino-modified graphene oxide (GONH 2 ) 17 . Most of previous studies required expensive chemical, multi-preparation steps, low adsorption capacities, delayed equilibrium period, see Table 1 .…”
Section: Introductionmentioning
confidence: 99%
“…These activated function groups consider as available negative active site that can form a complex with the cationic pollutants. In order to improve the adsorption efficiency of GO, numerous studies were investigated to liable GO in another constructures such as; graphene oxide (GO), sodium alginate (SA) and hydroxyethyl cellulose (HEC) (SA-HEC/GO bio-adsorbent hydrogel beads 8 , graphene oxide/hollow mesoporous silica (GO–HMS) composite 9 , sodium alginate/gelatin/graphene oxide (SGGO) nanocomposite 10 , polyaniline/graphene oxide (PANI/GO) nanocomposite 11 , graphene oxide-chitosan-EDTA (GO–EDTA–CS) nanocomposite 12 , polyethyleneimine (PEI) modified (GO) to form (GO/PEI) sponge 13 , decoration of GO with zinc oxide nanoparticles (ZnO) (GO/ZnO) 14 , graphene oxide (GO) modified with isocyanate (MDI), subsequently, (EDTA) (EDTA/MDI/GO) composite 15 , modification of graphene oxide (GO) nanosheets with magnetic particles of nickel ferrite (NiFe 2 O 4 ) and followed by immobilizing glutathione (GSH) to fabrication of GSH-NiFe 2 O 4 /GO nanocomposite 16 and Amino-modified graphene oxide (GONH 2 ) 17 . Most of previous studies required expensive chemical, multi-preparation steps, low adsorption capacities, delayed equilibrium period, see Table 1 .…”
Section: Introductionmentioning
confidence: 99%
“…To obtain a 3D porous structure and to improve the biological activity of GO, the scaffolds have been prepared by step-wise covalent growth of multilayer architectures of GO sheets alternated by linear polyethylenimine (PEI) macromolecules, the latter acting as linkers and spacers. Cross-linking between GO and PEI has been previously reported to form structurally defined foams with controlled porosity, , adsorbing sponge materials, and GO framework membranes for ion-selective separations . Here, we used for the first time such a cross-link synthetic procedure at interfaces by means of the covalent layer-by-layer (LbL) technique to generate controlled 3D architectures.…”
Section: Introductionmentioning
confidence: 99%
“…While any amine-rich polymer, such as chitosan and polyallylamine, can be considered as an effective component for copper-binding materials, branched polyethylenimine (PEI) possesses an exceptional copper-binding selectivity and capacity. , Although, as in all amines, the copper-binding capacity of PEI decreases with decreasing pH, it still remains significant down to pH ∼3 with exceptional selectivity for copper, in contrast to simple aliphatic amines, such as ethylenediamine, which hardly interacts with copper at pH ≤ 3. , The polymer itself remains stable even under very acidic conditions, allowing simple recovery of bound copper without use of any competing chelators. ,,, A number of highly efficient PEI-based composites have been developed for copper extraction from acidic solutions, including mining wastewaters. Just to name a few, PEI-modified montmorillonite, cross-linked PEI-diatomaceous earth particles, glutaraldehyde-PEI particulate resin, PEI-modified magnetic graphene oxide nanocomposites and graphene oxide/PEI sponges were all shown to repeatedly bind copper from acidic aqueous solutions, followed by full copper recovery via washing the copper-loaded materials at pH ∼1. However, the majority of PEI-based composites were designed and tested for application in aqueous solutions only, which restricts their use in harsh mixed media, such as aqueous slurries of comminuted ore or soils.…”
Section: Introductionmentioning
confidence: 99%
“…19,20,23,24 A number of highly efficient PEIbased composites have been developed for copper extraction from acidic solutions, including mining wastewaters. Just to name a few, PEI-modified montmorillonite, 25 cross-linked PEIdiatomaceous earth particles, 26 glutaraldehyde-PEI particulate resin, 27 PEI-modified magnetic graphene oxide nanocomposites 28 and graphene oxide/PEI sponges 29 were all shown to repeatedly bind copper from acidic aqueous solutions, followed by full copper recovery via washing the copper-loaded materials at pH ∼1. However, the majority of PEI-based composites were designed and tested for application in aqueous solutions only, which restricts their use in harsh mixed media, such as aqueous slurries of comminuted ore or soils.…”
Section: Introductionmentioning
confidence: 99%