CuFe 2 O 4 @CuO: A Magnetic Composite Synthesized by Ultrasound Irradiation and Degradation of Methylene Blue on Its Surface in the Presence of Sunlight

: Spinel ferrite MFe 2 O 4 (M = Cu, Ca, Mg, Ni, etc.) nanoparticles and their composites are a new promising materialbecause they have shown great interest in the field of sensing, optoelectronics, catalysis, and solar cells due to their unique physical and chemical properties that differ from their bulk structures. Today, lots of CuFe 2 O 4 nanomaterials have been synthesized by different methods, such as hydrothermal route and sol-gel combustion methods. Nevertheless, there are hardly any results about photocatalytic activity. For this reason, we tried to increase optical properties by preparing a composite of CuFe 2 O 4 nanomaterials with other oxides. In this paper, a CuFe 2 O 4 @CuO magnetic composite was synthesized via an ultrasound method. The samples prepared were characterized by X-ray diffraction (XRD), Fourier-transform infrared spectroscopy (FT-IR), diffuse reflectance spectrpscopy (DRS), field emission scanning electron microscopy (FESEM) images, vibrating sample magnetometer (VSM), and elemental analysis (energy-dispersive X-ray (EDX)). The catalytic activity of as-synthesized CuFe 2 O 4 @CuO was evaluated using the degradation of methylene blue. Furthermore, a possible reaction mechanism was discussed. Finally, the catalyst was used for effective degradation of methylene blue (MB) in its solution, which indicated a potential for practical applications in water pollutant removal and environmental remediation.


Introduction
In the last few years, metallic oxides and their mixed compounds (as called composites) have been considered as a green semiconductor photocatalyst to resolve the increasing energy and environmental crisis by using solar light sources for organic dye degradation and hydrogen generation from water [1][2][3][4][5]. When the single-component photocatalysts have a poor quantum efficiency and low photocatalytic performance, they are mixed with each other and a heterojunctiontype photocatalytic system is created. In recent years, this system has been used as part of an important strategy to overcome the drawbacks of a single photocatalyst, which modifies the yield of the photoexcited (electron-holes) separation [6,7]. Unfortunately, one of the disadvantages of these heterojunction systems is that the generation of the electron-hole pair is ordinarily weakened after a charge transfer [8]. Therefore, the high charge-separation efficiency and strong redox ability are difficult to possess at the same time. Recently, the concentration of a photocatalytic system with magnetic properties is an ideal and effective means because it not only can reduce the bulk electronhole recombination and preserved redox ability but it is also a green material [9].
Copper ferrites have been continuously investigated because of their properties (semiconducting, magnetic properties, thermal, and chemical stabilities). Nanosized copper spinel ferrite can be fabricated by a variety of methods such as ball-milling [10], sol-gel [11], and coprecipitation [12].
Copper oxide nanoparticles have attracted a lot of attention in various fields, particularly catalytic applications, because they possess appealing properties like non-toxicity, chemical stability, electrochemical activity, etc. Multiple morphologies and sizes of CuO nanoparticles have been synthesized by using different synthetic methods such as thermal evaporation, thermal decomposition, thermal oxidation, electrospinning, solid-liquid arc discharge processes, chemical vapor deposition, sol-gel method, etc. [13].
In this context, a magnetic composite (CuFe2O4@CuO) was prepared via ultrasound irradiation in the presence of ammonia solution and ethylene glycol. Also, we report on the photocatalytic degradation of methylene blue (MB) over CuFe2O4@CuO heterojunctions under visible light irradiation.

XRD Patterns
To identify the crystallinity and crystal phases of the CuO pearls, XRD analysis was performed and is shown in Figure 1B. Upon notification reflection peaks, only a pure monoclinic phase of CuO is presented in the prepared nanoparticles, which are in good agreement with the literature value (JCPDS card No. 05-0661).
XRD pattern for the magnetic composite (CuO@CuFe2O4) sample synthesized with ultrasound power and calcination temperature is depicted in Figure 1C. It is noted in this pattern that whole peaks are in accordance with the corresponding standard pattern of copper ferrite and the standard pattern of copper oxide, which confirm the presence of each one in the as-prepared composite.

FT-IR Study
The FT-IR transmission mode spectrum for everything synthesized (CuFe2O4, CuO, and CuO@CuFe2O4) was studied, as shown in Figure 2. According to the results, there is no observed additional adsorption peaks of each spectrum that indicates the presence of any byproduct or raw organic material used for the preparation. The existence of CO2 molecule over a compound's surface was verified by the weak absorption peak observed around 2333.43 cm −1 .

Morphological Analysis of CuFe2O4, CuO and Their Composite
The FESEM micrograph of CuFe2O4 nanospheres that grew under solvothermal conditions is shown in Figure 3A,B. These particles have a sphere-like structure with an approximate average size of 170-195 nm. Further, the homogeneous distribution of copper ferrite nanospheres has led to enhancing the density of its surface. The aggregation of the copper ferrite nanosphere is not large. Figure 3C,D shows the structural morphology of the CuO nanostructure that was prepared via pyrolysis/hydrolysis of copper (II) nitrate in an ethylene glycol/ammonia solution with ultrasound irradiation in ambient air. The morphology of these synthesized particles were pearl with a smooth surface. Average particle size varied fin 25-35 nm range. Figure 3E,F reveals the FESEM image of the typical CuO@CuFe2O4 magnetic composite. These images confirmed that the morphological structure of the product is close to spherical but not uniform with various sizes. Moreover, there are agglomerated particles in some sites, which can be attributed to many factors (i.e., high annealing temperature, the presence of electrostatic, and Van der Waals forces between magnetic particles). In addition, it was noted that a number of small nanoparticles of copper oxide uniformly covered the surfaces of CuFe2O4 on a large scale (~310 nm).

Elemental Analysis
The composition analysis of CuO@CuFe2O4 was examined through an energy dispersive analysis (EDX) spectrum, as depicted in Figure 4 which confirms the existence of O, Fe, and Cu elements. The atomic percentage of the elements is nearly close to stoichiometry value. The experimental values of the atomic percentage have some copper insufficiency.

VSM Analysis
The hysteresis loop of CuFe2O4 and CuO@CuFe2O4 nanoparticles is shown in Figure 5A,B. The saturation magnetization values of CuO@CuFe2O4 were found to be lower than the corresponding CuFe2O4. The value of saturation magnetization values of CuFe2O4 (Ms = 86.41 emu/g) is compared to that of CuO@CuFe2O4 (Ms = 72.58 emu/g) and can be expressed in the basis of a homogeneous covering model that explains the narrow distribution of densely covered CuO on copper ferrite surfaces that resulted in reducing magnetization. Moreover, the magnetic moment was reduced by increasing the particles size and sintering the temperature.

Photocatalytic Activity
The photocatalytic activity of pure oxides and CuO@CuFe2O4 catalysts under sunlight irradiation was defined by measuring the photodegradation of methylene blue (MB) aqueous solutions. Methylene blue (MB) is a cationic dye with a methyl nitride group [(CH3)2N + ]. Figure 6A,B illustrates the comparison of the photocatalytic activity of CuFe2O4, CuO, and CuO@CuFe2O4 composite for the degradation of methylene blue (MB) (10 mg L −1 ) under sunlight irradiation for 3 h. In order to investigate the adsorption properties for the photocatalysts, its working in dark was tested. Under sunlight irradiation, the results show that the degradation yield of methylene blue (MB) in the presence of CuO, CuFe2O4, and CuO@CuFe2O4 samples was 18%, 36%, and 90%, respectively. However, these values were 8% (CuO), 13% (CuFe2O4), and 42% composite in the dark ( Figure 6B). Thus, the CuO@CuFe2O4 composite displays a better degradation performance of methylene blue (MB) rather than pure oxides in the same condition. Surprisingly, pristine CuO was very low and had sluggish degradation behavior, which can be attributed to the very recombination rates of (electron-hole) pairs in pure oxides and also the absence of the second material, such as copper ferrite for a charge transfer. However, the adsorption results for samples were also not credible.
Moreover, Figure 7 displays the comparison of the methylene blue (MB) removal yield in various times. CuO@CuFe2O4 was under sunlight irradiation and in dark. The obtained results illustrate that the MB decomposed 90% in 120 min under sunlight irradiation and was adsorbed only 42% after 90 min in the dark. Therefore, the final composite is as an excellent photocatalyst for degradation of the dye under sunlight irradiation.

Preparation of the CuO@CuFe2O4 Nanocomposite
Firstly, 0.12 g of FeCl3·6H2O and 0.0511 g of CuCl2·2H2O were added into 15 mL of an ethylene glycol (EG) solution. Then, 0.2 g of ammonium acetate (CH3COONH4) was added into the mixture under vigorous stirring. This solution was sonicated for 30 min. Subsequently, the homogenous mixture was transferred into a Teflon-lined stainless-steel autoclave with 40 mL capacity and heated at 200 °C for 20 h.
A solid powder of the CuO@CuFe2O4 nanocomposite was synthesized using an ultrasound method under an ambient condition. Next, 0.525 g of copper ferrite and 5 mL of ethylene glycol were well-mixed and sonicated for 25 min using an ultrasonic. Afterward, 0.575 g of copper nitrate (Cu(NO3)2·H2O) was dissolved into 25 mL of DI H2O and was slowly dispersed into the copper ferrite/EG mixture. During sonication, 15 mL of ammonia solution (25%) was added to adjust the pH to 11. After sonication, the product was gathered by centrifugation and washed by ethanol and deionized water (DI), which removed any organic materials that adsorbed on the surface. After that, the nanocomposite was dried at 70 °C, pinpointed in crucible, and calcined at 200 °C for 2 h.

Photocatalytic Experiments
Photocatalytic activity of the prepared CuFe2O4 nanospheres, CuO nanopearls, and CuO@CuFe2O4 magnetic composite was evaluated with photodegradation of MB solutions. In the experimental set-up, 0.01 g of photocatalyst was added to a 100 mL photoreactor containing 10 mL of MB dye (10 mg·L −1 ). In order to obtain an equilibrium point for the initial physical adsorption of MB over the sample surface, the solution was stirred in the dark for 30 min. Then, the container was placed under sunlight for about 3 h. All photocatalytic experiments were carried out in the same conditions. The percentage of removal efficiency (X%) is given by: where C0 is the concentration of dye at 0 minute and C is the concentration of dye at time t.

Conclusions
A superparamagnetic CuO@CuFe2O4 composite with spherical morphology was successfully synthesized with low-cost precursors and a simple sonication technique. The improved catalytic activity of CuO@CuFe2O4 was explored on the basis of a tailored band gap and chemical interaction between CuFe2O4 and CuO, leading to a fast charge transport through the interfacial layers. This inhibited the charge recombination (e-/h+ pairs) and ensured accessibility for free charge carriers to support the catalytic activity. Room temperature magnetization outcomes revealed a superparamagnetic behavior of the as-synthesized CuFe2O4 and CuO@CuFe2O4, indicating that this nanocomposite can be a usable photocatalyst due to its efficient magnetic separation.