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. 2018 Jan 3;8(2):1089-1097.
doi: 10.1039/c7ra12240c. eCollection 2018 Jan 2.

Highly stable mesoporous silica nanospheres embedded with FeCo/graphitic shell nanocrystals as magnetically recyclable multifunctional adsorbents for wastewater treatment

Affiliations

Highly stable mesoporous silica nanospheres embedded with FeCo/graphitic shell nanocrystals as magnetically recyclable multifunctional adsorbents for wastewater treatment

Yonghoon Hong et al. RSC Adv. .

Abstract

Highly stable and magnetically separable mesoporous silica nanospheres (MSNs) embedded with 4.6 ± 0.8 nm FeCo/graphitic carbon shell nanocrystals (FeCo/GC NCs@MSNs) were synthesized by thermal decomposition of metal precursors in MSNs and subsequent methane CVD. The FeCo/GC NCs@MSNs had a high specific surface area (442 m2 g-1), large pore volume (0.65 cm3 g-1), and tunable size (65 nm, 130 nm, and 270 nm). Despite the low magnetic metal content (8.35 wt%), the FeCo/GC NCs@MSNs had a sufficiently high saturation magnetization (17.1 emu g-1). This is due to the superior magnetic properties of the FeCo/GC NCs, which also enable fast magnetic separation of the nanospheres. The graphitic carbon shell on the FeCo NCs not only protects the alloy core against oxidation and acid etching in 35% HCl(aq), but also facilitates non-covalent, hydrophobic interactions with the hydrocarbon chains of organic dyes such as methyl orange and methylene blue. Surface functionalization of the FeCo/GC NCs@MSNs with thiol groups provides efficient capacity for binding with Hg2+ ions. We have shown that the thiol-functionalized FeCo/GC NCs@MSNs (FeCo/GC NCs@MSNs-SH) work as multifunctional adsorbents for organic dyes (target organic pollutants) and Hg2+ ions (target inorganic pollutant). We also demonstrated that the FeCo/GC NCs@MSNs-SH are excellent recyclable adsorbents for methyl orange.

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Conflict of interest statement

There are no conflicts to declare.

Figures

Fig. 1
Fig. 1. Schematic illustration for the preparation of FeCo/GC NCs@MSNs-SH and the multifunctional adsorption of organic dyes and mercury(ii) ions.
Fig. 2
Fig. 2. TEM images of (a, b) 65 nm, (c, d) 130 nm, and (e, f) 270 nm MSNs (a, c, e), and FeCo/GC NCs@MSNs (b, d, f). Insets in Fig. 2b, d, and f are SAED patterns. (g) XRD patterns of 65 nm, 130 nm, and 270 nm FeCo/GC NCs@MSNs.
Fig. 3
Fig. 3. (a) Nitrogen sorption isotherms and (b) pore size distributions of 130 nm MSNs and FeCo/GC NCs@MSNs.
Fig. 4
Fig. 4. (a) Illustration of thiol functionalization reaction between MPTMS and silanol groups on the silica surface. (b) FT-IR and (c) TGA data of 130 nm FeCo/GC NCs@MSNs and FeCo/GC NCs@MSNs-SH.
Fig. 5
Fig. 5. Adsorption isotherms of (a) MB and (c) MO for MSNs (squares), FeCo/GC NCs@MSNs (circles), and FeCo/GC NCs@MSNs-SH (triangles) in water (the solid lines represent the best fit of the experimental data to the Langmuir model). Adsorption curves of (b) MB and (d) MO for MSNs (squares), FeCo/GC NCs@MSNs (circles), and FeCo/GC NCs@MSNs-SH (triangles) in water as a function of contact time.
Fig. 6
Fig. 6. Photographs of aqueous solutions of (a) MB and (d) MO and the FeCo/GC NCs@MSNs-SH collected using a magnet in the aqueous solutions after the adsorption of the organic dyes, MB (b) and MO (c).
Fig. 7
Fig. 7. Regeneration study of FeCo/GC NCs@MSNs-SH for the adsorption of MO in water at room temperature.

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