2021
DOI: 10.1016/j.apsusc.2021.150931
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Efficient adsorption and reduction of Cr(VI) and U(VI) by nanoscale zero-valent iron supported on polydopamine-decorated SBA-15

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Cited by 51 publications
(10 citation statements)
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“…The adsorption of U­(VI) on MoS 2 and nZVI/MoS 2 gradually increased with the increase of pH from 2.0 to 6.0 and reached the highest removal at pH 6.0–9.0 (92 and 95.0% for MoS 2 and nZVI/MoS 2 , respectively). However, the decreased removal of U­(VI) at pH >10 was observed, which was similar to previous studies. The pH-dependent removal of U­(VI) on nZVI/MoS 2 can be interpreted by the electrostatic interaction between U­(VI) and adsorbents. The low adsorption of U­(VI) on nZVI/MoS 2 and MoS 2 at low pH could be due to the electrostatic repulsion of positively charged adsorbents and positive UO 2 2+ , while the decreased adsorption of U­(VI) at high pH can also be interpreted by electrostatic repulsion of negatively charged adsorbents and negative U­(VI) species such as UO 2 (CO 3 ) 2 2– and UO 2 (CO 3 ) 3 4– species.…”
Section: Resultssupporting
confidence: 89%
“…The adsorption of U­(VI) on MoS 2 and nZVI/MoS 2 gradually increased with the increase of pH from 2.0 to 6.0 and reached the highest removal at pH 6.0–9.0 (92 and 95.0% for MoS 2 and nZVI/MoS 2 , respectively). However, the decreased removal of U­(VI) at pH >10 was observed, which was similar to previous studies. The pH-dependent removal of U­(VI) on nZVI/MoS 2 can be interpreted by the electrostatic interaction between U­(VI) and adsorbents. The low adsorption of U­(VI) on nZVI/MoS 2 and MoS 2 at low pH could be due to the electrostatic repulsion of positively charged adsorbents and positive UO 2 2+ , while the decreased adsorption of U­(VI) at high pH can also be interpreted by electrostatic repulsion of negatively charged adsorbents and negative U­(VI) species such as UO 2 (CO 3 ) 2 2– and UO 2 (CO 3 ) 3 4– species.…”
Section: Resultssupporting
confidence: 89%
“…Remedial efforts employing nZVI via reduction have been performed on 1,2-dichloroethylene (DCE), 28 trichloroethylene (TCE), [29][30][31][32] perchloroethylene (PCE), 28 1,1,1-trichloro-2,2-bis(4-chlorophenyl) ethane (DDT), 33 2,4-dichlorophenol (2,4-DCP), [34][35][36][37] trichloronitromethane (TCNM), 38 1,2,4-trichlorobenzene (1,2,4-TCB), 39 2,4,6-trichlorophenol (TCP), 40,41 2chlorobiphenyl (PCB1), 42,43 diclofenac (DCF), 44 chlorinated organophosphate esters (Cl-OPEs), 45 2,2 0 ,4,4 0 -tetrabromodiphenyl ether (BDE-47), 46,47 tetrabromobisphenol A (TBBPA), 48,49 methylene blue, 50 p-nitrophenol, 51,52 nitrobenzene, 53,54 mono-brominated diphenyl ether (BDE-3), 55 Cr(VI), [56][57][58][59][60][61] Sb(V), 62 Ni(II), [63][64][65][66] Pb(II), 65,67 Cu(II), 68 As(V), 69 U(VI), 23,[70][71]...…”
Section: Chemical Reduction By Nzvimentioning
confidence: 99%
“…16F-J). 23,71 The competitive adsorption of U(VI) and Cr(VI) can occur in an insufficient adsorption sites situation, which may result in low removal efficiency. 71…”
Section: Hcromentioning
confidence: 99%
“…Besides, loading the metal nanoparticles onto SBA-15 to form nanocomposites have been used for removal of heavy metals from water. For example, nanoscale zero-valent iron (nZVI) composites by loading into polydopamine (PDA)decorated SBA-15 exhibited the excellent removal capacity of Cr(VI) and U(VI) from aqueous solutions (Liu et al 2021). Moreover, the SBA-15@Fe/Ni composite prepared via loading nZVI onto SBA-15 as a support, showed the enhanced stability and removal capacity for Cr(VI) adsorption and reduction (Xing et al 2023).…”
Section: Introductionmentioning
confidence: 99%