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. 2023 Apr 6;13(16):10940-10955.
doi: 10.1039/d3ra00057e. eCollection 2023 Apr 3.

Synthesis of magnetic graphene-like carbon nitride-cobalt ferrite (g-C3N4/CoFe2O4) nanocomposite for sonocatalytic remediation of toxic organic dyes

Affiliations

Synthesis of magnetic graphene-like carbon nitride-cobalt ferrite (g-C3N4/CoFe2O4) nanocomposite for sonocatalytic remediation of toxic organic dyes

Saeedeh Hassanzadeh et al. RSC Adv. .

Abstract

A novel magnetic g-C3N4/CoFe2O4 nanocomposite was successfully synthesized by a simple hydrothermal method and applied as a new graphene-like carbon nitride-based sonocatalyst for sonodegradation of pollutant dyes. The as-prepared samples were characterized by using X-ray diffraction (XRD), Fourier transform infrared (FT-IR) spectroscopy, field-emission scanning electron microscopy (FE-SEM), energy-dispersive X-ray spectroscopy (EDX), transmission electron microscopy (TEM), vibrating sample magnetometry (VSM), X-ray photoelectron spectroscopy (XPS), UV-visible diffuse reflectance spectroscopy (DRS), BET surface area measurements and photoluminescence (PL) spectroscopy. The results indicate that the nanocomposite sample is composed of spherical CoFe2O4 nanoparticles adhered to g-C3N4 naosheets. The g-C3N4/CoFe2O4 nanocomposites were used as a new magnetically separable sonocatalyst in H2O2-assisted sonodegradation of methylene blue (MB), rhodamine B (RhB) and methyl orange (MO) dyes in aqueous media. The results showed complete degradation (ca. 100%) of dyes within short times (30-35 min). The sonocatalytic activity of graphitic carbon nitride (g-C3N4) was greatly enhanced with CoFe2O4 modification. Trapping experiments indicated that the g-C3N4/CoFe2O4 nanocomposites serves as a generator of hydroxyl radical (˙OH) via activation of H2O2 for degradation of dyes under ultrasound irradiation. Furthermore, the magnetic sonocatalyst can be separated from solution by an external magnet and reused several times without observable loss of activity. The possible mechanism of sonocatalytic activity was also proposed according to experimental results.

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Conflict of interest statement

There are no conflicts of interest to declare.

Figures

Scheme 1
Scheme 1. The preparation process of the g-C3N4/CoFe2O4 nanocomposite.
Fig. 1
Fig. 1. FT-IR spectra of (a) C3N4, (b) CoFe2O4 and (c) g-C3N4/CoFe2O4 samples.
Fig. 2
Fig. 2. XRD patterns of (a) g-C3N4, (b) CoFe2O4 and (c) g-C3N4/CoFe2O4 samples.
Fig. 3
Fig. 3. FE-SEM images of (a) CoFe2O4, (b) g-C3N4, and (c and d) the g-C3N4/CoFe2O4 hybrid nanocomposite.
Fig. 4
Fig. 4. (a) The EDX spectrum and (b) elemental mappings of g-C3N4/CoFe2O4 nanocomposite.
Fig. 5
Fig. 5. The TEM images of the g-C3N4/CoFe2O4 nanocomposite.
Fig. 6
Fig. 6. XPS of the g-C3N4/CoFe2O4 nanocomposite: (a) survey spectrum, (b) Co 2p spectrum, (c) Fe 2p spectrum, (d) O 1S spectrum, (e) N 1S spectrum and (f) C 1S spectrum.
Fig. 7
Fig. 7. UV-vis DRS spectra of (a) g-C3N4, (b) CoFe2O4 and (c) g-C3N4/CoFe2O4 nanocomposite.
Fig. 8
Fig. 8. Room-temperature magnetization curves of (a) CoFe2O4 and (b) g-C3N4/CoFe2O4 nanocomposite (inset: the magnetic separation of g-C3N4/CoFe2O4 nanocomposite by a magnet).
Fig. 9
Fig. 9. N2 adsorption–desorption isotherms of (a) C3N4 and (b) g-C3N4/CoFe2O4 nanocomposite. The insets are the pore size distribution curves.
Fig. 10
Fig. 10. (a) The UV-vis absorption changes, (b) concentration changes (Ct/C0), and (c) the pseudo-first-order plots of −ln(Ct/C0) as a function of irradiation time for MB sonodegradation in the presence of g-C3N4/CoFe2O4 nanocomposite. Conditions: [MB]0 = 25 mg L−1,50 mL; [H2O2 ] = 0.1 mol L−1, 1 mL; [cat.] = 0.66 g L−1 at room temperature and natural pH = 7.
Fig. 11
Fig. 11. Effects of (a) different enhancers, (b) the H2O2 amount, (c) the g-C3N4/CoFe2O4 sonocatalyst dosage, and (d) initial dye concentration on the sonocatalytic degradation of MB in the presence of g-C3N4/CoFe2O4 nanocomposite. Conditions: [MB]0 = 25 mg L−1,50 mL; [enhancer] = 0.1 mol L−1, 1 mL; [cat.] = 0.66 g L−1 at room temperature and natural pH = 7.
Fig. 12
Fig. 12. The UV-vis absorption spectra changes of (a) rhodamine B (RhB), (b) methyl orange (MO), and (c) comparison of sonodegradation efficiency of dyes as a function of time over the g-C3N4/CoFe2O4 nanocomposite. Conditions: [dye] = 25 mg L−1, 50 mL; [cat.] = 0.66 g L−1; [H2O2] = 0.1 mol L−1, 1 mL; at room temperature and natural pH = 7.
Fig. 13
Fig. 13. (a) Effects of different scavengers on the sonocatalytic degradation of MB. Conditions: [MB] = 25 mg L−1, 50 mL; [cat.] = 0.66 g L−1; [H2O2] = 0.1 mol L−1, 1 mL; [scavenger] = 0.1 mol L; at room temperature and natural pH = 7. (b) Schematic illustration of the possible sonocatalytic mechanism of the g-C3N4/CoFe2O4 nanocomposite under ultrasound irradiation.
Fig. 14
Fig. 14. PL spectra of (a) pure g-C3N4 and (b) g-C3N4/CoFe2O4 samples.
Fig. 15
Fig. 15. (a) Cycling runs of g-C3N4/CoFe2O4 nanocomposite in the sonodegradation of MB. Each run of photocatalytic reactions lasted for 30 min. (b) FT-IR spectrum, (c) XRD pattern and (d) TEM image (e) SEM image of the recovered nanocomposite after the 5th run.

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