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. 2018 Nov 12;8(66):37976-37992.
doi: 10.1039/c8ra06287k. eCollection 2018 Nov 7.

K6P2W18O62 encapsulated into magnetic Fe3O4/MIL-101 (Cr) metal-organic framework: a novel magnetically recoverable nanoporous adsorbent for ultrafast treatment of aqueous organic pollutants solutions

Affiliations

K6P2W18O62 encapsulated into magnetic Fe3O4/MIL-101 (Cr) metal-organic framework: a novel magnetically recoverable nanoporous adsorbent for ultrafast treatment of aqueous organic pollutants solutions

Afsoon Jarrah et al. RSC Adv. .

Abstract

In this study, a Wells-Dawson type K6P2W18O62 polyoxometalate was encapsulated into the magnetic Fe3O4/MIL-101 (Cr) metal-organic framework and applied as a new magnetically recoverable ternary adsorbent to remove organic dyes from aqueous solutions. The as-prepared ternary magnetically recyclable hybrid (denoted as P2W18O62@Fe3O4/MIL-101 (Cr)) was characterized by FT-IR spectroscopy, powder X-ray diffraction (XRD), Raman spectroscopy, EDX, SEM, BET surface area, and magnetic measurements. The results showed the successful encapsulation of K6P2W18O62 (∼26.5 wt%) into the magnetic Fe3O4/MIL-101 (Cr) framework. The magnetic hybrid had a high specific surface area of 934.89 m2 g-1. The adsorption efficiency of this nanohybrid for the removal of methylene blue (MB), rhodamine B (RhB), and methyl orange (MO) from aqueous solutions was evaluated. The magnetic nanohybrid demonstrated the fast and selective adsorption of cationic dyes from mixed dye solutions. The adsorption rate and capacity of P2W18O62@Fe3O4/MIL-101 (Cr) were increased as compared with MIL-101 (Cr), P2W18O62, and Fe3O4/MIL-101 samples due to the increased electrostatic attraction. The effects of parameters such as the adsorbent dosage, temperature, dye concentration, and pH were investigated on the adsorption process. The adsorption kinetics was analyzed by the Freundlich, Langmuir, and Temkin isotherm models and pseudo-second-order and pseudo-first-order kinetics models, with the Langmuir isotherm and pseudo-second-order kinetic model found to be suitable to describe the equilibrium data. Also, the thermodynamic results of the nanohybrid indicated that the adsorption was an endothermic and spontaneous process. After the adsorption reaction, the magnetic nanohybrid could be easily separated and reused without any change in structure. Based on the results of this study, the nanohybrid was an efficient adsorbent for eliminating cationic dyes.

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Conflict of interest statement

There are no conflicts of interest to declare.

Figures

Fig. 1
Fig. 1. FT-IR spectra of (a) MIL-101 (Cr), (b) P2W18O62, (c) Fe3O4 (d) P2W18O62@MIL-101 (Cr), (e) Fe3O4/MIL-101 (Cr), and (f) P2W18O62@Fe3O4/MIL-101 (Cr).
Fig. 2
Fig. 2. XRD patterns of (a) MIL-101 (Cr), (b) P2W18O62, (c) Fe3O4, (d) P2W18O62@MIL-101 (Cr), (e) Fe3O4/MIL-101 (Cr), and (f) P2W18O62@Fe3O4/MIL-101 (Cr).
Fig. 3
Fig. 3. Raman spectra of (a) MIL-101 (Cr), (b) P2W18O62, (c) P2W18O62@MIL-101 (Cr), (d) P2W18O62@Fe3O4/MIL-101 (Cr).
Fig. 4
Fig. 4. SEM images of (a and b) MIL-101 (Cr), (c and d) P2W18O62@MIL-101 (Cr), (e and f) Fe3O4/MIL-101 (Cr), and (g and h) P2W18O62@Fe3O4/MIL-101 (Cr).
Fig. 5
Fig. 5. (a) EDX spectrum, and (b)–(i) a representative SEM image of the P2W18O62@Fe3O4/MIL-101 (Cr) magnetic nanohybrid with corresponding EDX elemental mappings.
Fig. 6
Fig. 6. (a) Nitrogen adsorption–desorption isotherm and (b) pore-size distributions of MIL-101 (Cr), P2W18O62@MIL-101 (Cr), and P2W18O62@ Fe3O4/MIL-101 (Cr) nanohybrid.
Fig. 7
Fig. 7. Magnetic hysteresis loop of (a) Fe3O4, (b) Fe3O4/MIL-101 (Cr), and (c) P2W18O62@Fe3O4/MIL-101 (Cr) at room temperature. The inset shows the behavior of the nanohybrid under an external magnetic field.
Fig. 8
Fig. 8. UV-Vis spectral changes of dyes aqueous solutions with P2W18O62@Fe3O4/MIL-101 (Cr) at different time intervals: (a) MB dye, (b) RhB dye. [Dye] = 25 mg L−1, adsorbent: 30 mg at 25 °C.
Fig. 9
Fig. 9. Effect of (a) pH, (b) adsorbent dosage, (c) dye concentration, and (d) different temperatures on the removal of MB and RhB dyes.
Fig. 10
Fig. 10. Effects of different loading amounts of P2W18O62 in MIL-101 (Cr) on the removal of MB and RhB dyes.
Fig. 11
Fig. 11. Adsorption efficiency of MB and RhB dyes in the presence of different adsorbent samples.
Fig. 12
Fig. 12. Selective adsorption ability of P2W18O62@Fe3O4/MIL-101 (Cr) toward mixed dyes solution of (a) MB&MO, (b) MB&RhB, (c) RhB&MO, (d) MB&RhB&MO. Conditions: C0 (MB) = C0 (RhB) = C0 (MO) = 25 mg L−1, and adsorbent dose = 30 mg/30 mL.
Fig. 13
Fig. 13. Effect of contact time and initial dye concentration on the adsorption process onto the P2W18O62@Fe3O4/MIL-101 (Cr) adsorbent.
Fig. 14
Fig. 14. Pseudo-second order kinetics for dyes adsorption: (a) MB, (b) RhB.
Fig. 15
Fig. 15. (a) Recyclability of the P2W18O62@Fe3O4/MIL-101 (Cr) hybrid nanomaterial in the removal of MB dye, (b) SEM images, (c) FT-IR spectrum, and (d) XRD pattern of the fresh and recovered nanohybrid after three runs.

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