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. 2024 Sep;11(36):e2402018.
doi: 10.1002/advs.202402018. Epub 2024 Jun 17.

Polyoxometalate Clusters Confined in Reduced Graphene Oxide Membranes for Effective Ion Sieving and Desalination

Affiliations

Polyoxometalate Clusters Confined in Reduced Graphene Oxide Membranes for Effective Ion Sieving and Desalination

Yixin Yang et al. Adv Sci (Weinh). 2024 Sep.

Abstract

Efficient 2D membranes play a critical role in water purification and desalination. However, most 2D membranes, such as graphene oxide (GO) membranes, tend to swell or disintegrate in liquid, making precise ionic sieving a tough challenge. Herein, the fabrication of the polyoxometalate clusters (PW12) intercalated reduced graphene oxide (rGO) membrane (rGO-PW12) is reported through a polyoxometalate-assisted in situ photoreduction strategy. The intercalated PW12 result in the interlayer spacing in the sub-nanometer scale and induce a nanoconfinement effect to repel the ions in various salt solutions. The permeation rate of rGO-PW12 membranes are about two orders of magnitude lower than those through the GO membrane. The confinement of nanochannels also generate the excellent non-swelling stability of rGO-PW12 membranes in aqueous solutions up to 400 h. Moreover, when applied in forward osmosis, the rGO-PW12 membranes with a thickness of 90 nm not only exhibit a high-water permeance of up to 0.11790 L m-2 h-1 bar-1 and high NaCl rejection (98.3%), but also reveal an ultrahigh water/salt selectivity of 4740. Such significantly improved ion-exclusion ability and high-water flux benefit from the multi-interactions and nanoconfinement effect between PW12 and rGO nanosheets, which afford a well-interlinked lamellar structure via hydrogen bonding and van der Waals interactions.

Keywords: desalination; ion sieving; membranes; polyoxometalates; reduced graphene oxide.

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Conflict of interest statement

The authors declare no conflict of interest.

Figures

Figure 1
Figure 1
a) The scheme of the fabrication of rGO‐PW12 membranes through a PW12 assisted in situ photoreduction strategy. b) SEM image of the top view of the rGO‐PW12 membranes. (inset: digital photo) c–f) SEM images of the cross‐section of rGO‐PW12 membranes with different thicknesses. g) HRTEM image of highly ordered nanochannels of rGO‐PW12 membranes with one orientation. The yellow dashed arrows were eye‐guiding lines indicating the orientations of rGO. h) HRTEM image of PW12 cluster in rGO‐PW12 nanosheets. i) HAADF‐STEM image of rGO‐PW12 nanosheets. j) Magnified HAADF‐STEM images of PW12 cluster indicated by the dashed circle in Figure 1i. (inset: corresponding EDX line scanning of PW12 cluster and the polyhedron of PW12 cluster).
Figure 2
Figure 2
a) Raman spectra of GO and rGO‐PW12 membranes. b) C 1s high‐resolution XPS spectra of GO and rGO‐PW12 membranes. c) W high‐resolution XPS spectra of rGO‐PW12 membrane and PW12. d) FT‐IR spectra of rGO‐PW12 membrane and PW12. e) The electron density difference of rGO‐PW12. The yellow and blue regions indicated the charge accumulation and depletion, respectively. (isosurface value: 0.02 e Å−3) The curved arrows indicated the electronic transfer from rGO to PW12. f) Isosurface and g) scatter graph of independent gradient model (IGM) for unveiling the interaction between rGO and PW12, C‐cyan, H‐white, O‐red, W‐pink, P‐olive drab. (inset: the schematic diagram showed that PW12 was tightly bound to rGO nanosheets).
Figure 3
Figure 3
a) Schematic diagram for GO and rGO‐PW12 membranes structures. b) XRD patterns of pristine GO and rGO‐PW12 membranes in dry and wet states. c) Membrane stability test. d) The water contact angle of GO and rGO‐PW12 membranes.
Figure 4
Figure 4
Ion permeation tests through GO and rGO‐PW12 membranes Feed solutions of 0.1 m KCl, NaCl, LiCl, MgCl2, CaCl2, and AlCl3 were used in draw side, while DI water filled the permeate side, respectively. a) Scheme of rGO‐PW12 membranes how to realize controllable ion transport. b,c) Comparison of the permeation rate of ions through GO and rGO‐PW12 membranes. d) The dependence of permeation rate on the mass ratio of rGO:PW12 for NaCl and MgCl2. MD simulation snapshots at 0 and 35 ns for two sets of Na+ and Cl permeation systems: untreated GO (e) and rGO‐PW12 (f) membranes. g) The number of ions that passed through the membranes as a function of simulation time.
Figure 5
Figure 5
a) Cycles of desalination/drying performance of rGO‐PW12 membranes. b) Long‐term Na+ permeation rate through GO and rGO‐PW12 membranes. (Inset: accumulated permeated Na+ along with testing time.) c) Comparison of permeation rate of ions in synthetic seawater through GO and rGO‐PW12 membranes. The synthetic seawater was a mixture of KCl, 0.0093 m; NaCl, 0.42 m; Na2SO4, 0.029 m; CaCl2·2H2O 0.011M  and MgCl2·2H2O, 0.056 m. (Inset: Rejection rate for each cation.) d) Chlorine resistance of GO and rGO‐PW12 membranes. Na+ permeation rate and rejections (inset) through the GO and rGO‐PW12 membranes before and after NaClO (200 ppm) treatment for 48 h. e) Salt permeation rate and water flux of GO and rGO‐PW12 membranes with different thicknesses under osmotically driven pressure. f) Water permeance and NaCl rejection performance of different 2D laminar membranes using osmotically driven pressure. The detailed data are listed in Table S3 (Supporting Information).
Figure 6
Figure 6
Schematic representation of efficient ion sieving (K+ or Mg2+) by the 2D rGO‐PW12 membranes.

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