Synthesis of ZnO-NiFe 2 O 4 Magnetic Nanocomposites by Simple Solvothermal Method for Photocatalytic Dye Degradation under Solar Light

ZnO-NiFe2O4 magnetic nanocomposite photocatalysts were successfully synthesized by simple solvothermal method using nitric salts as starting materials and ethanol as solvent. The synthesized samples were characterized by XRD, FESEM-EDX, TEM, DRS-UV-vis, VSM, and FTIR instruments. Photocatalytic activity of the samples was evaluated by dye degradation under solar light irradiation. The results show that the diffraction peaks of nanocomposites correspond to the hexagonal wurzite of ZnO and spinal cubic structure of NiFe2O4. The microstructure studies revealed that nanocomposites were dominated by granular-like of ZnO nanoparticles were synthesized at 180°C and rod-like at 200°C. The estimated band gap value of ZnO-NiFe2O4 (1:0.01) nanocomposites is 2.78 eV which is lower than ZnO. The magnetic saturation (Ms) result showed a superparamagnetic behavior for nanocomposites. It was found that the photocatalytic activity of synthesized nanocomposites were higher than ZnO and NiFe2O4.


INTRODUCTION
Semiconductors are particularly useful as photocatalysts due to a favorable combination of electronic structure, light absorption properties, and excited-state lifetimes 1 .Among various semiconductors employed, zinc oxide (ZnO) is well known to be an excellent photocatalyst [2][3] .Some researchers have reported that ZnO as photocatalyst exhibit superior advantages than the others, which is ascribed to its higher quantum efficiency, chemical stability, non-toxicity, and lower cost 4,5 .Unfortunately, ZnO has a wide band gap (~3.37 eV), which is unfavorable for absorption well of visible light of solar 6,7 .In fact, visible light contributes more than 50% of the sun irradiation and it is important to fabricate an excellent visible-light response photocatalyst for the practical uses 8 .To improve the performance of ZnO several attempts have been made to shift its absorption band from UV to visible light region such as doping or coupling ZnO with metals, non metals, and metal oxides [9][10][11] .However, the difficulty in separating of those ZnObased photocatalysts from aqueous solutions limits their application in dyes waste water treatment 12 .One of the effective strategies to solve the problem is to prepare the magnetic photocatalysts with well recyclability by coupling of ZnO   The nickel ferrite (NiFe 2 O 4 ) is one of the most important spinal ferrites due to cubic inverse-spinalbased structure, high saturation magnetization, and narrow band gap (1.6 eV) 16,17 .Coupling between ZnO and NiFe 2 O 4 forming a semiconductor photocatalysts which enhanced activity under visible light.Theoretically, when ferrite materials are coupled with ZnO, the heterojunction formed and then the photogenerated electrons and holes were separated efficiently, leading to enhancement in photocatalytic activity 18,19 .Furthermore, the presence of magnetic spinal ferrite facilitates the recycling process of these photocatalysts because they are able to be separated easily by external magnetic field after photocatalytic reactions.This ferrite has been successfully used to improve the activity of TiO 2 in the visible light region 20,21 .
Recently, NiFe 2 O 4 /ZnO hybrid nanoparticles were synthesized by ultrasonic treatment and hydrothermal method and applied for decolorization of Congo red has been reported 22 .Ferromagnetic NiFe 2 O 4 /ZnO hybrid nanoparticles prepared by the hydrolysis of zinc acetate in the presence of NiFe 2 O 4 in w/o microemulsion, using CTAB as the surfactant, n-pentanol as the cosurfactant, cyclohexane as the oil phase have also been reported 23 .In this present work ZnO-NiFe 2 O 4 nanocomposites were synthesized by simple solvothermal method using nitric salts as starting materials and ethanol as solvent.The activity of the samples was evaluated by photocatalytic degradation of Rhodamine B dye under solar light irradiation.The influence of operating parameters on the photodegradation, namely the amount of NiFe 2 O 4 , catalyst loading, reaction temperature, and the length of exposure time were investigated.

MATERIALS AND METHODS
The chemicals and reagents were used in this work are Ni(NO 3 ) 2 .6H 2 O, Fe(NO 3 ) 3 .9H 2 O, Zn(NO 3 ) 2 .4H 2 O, NaOH, ethanol p.a. (all materials purchased from Merck), and Rhodamine B. All reagents were analytically pure and used without further purification.

Synthesis of NiFe 2 O 4 nanoparticles
The nanoparticles of NiFe 2 O 4 were obtained by dissolved 10 mmol Ni(NO 3 ) 2 .6H 2 O and 20 mmol Fe(NO 3 ) 3 .9H 2 O in 100 mL distilled water and mixed under magnetic stirring for 30 min.Then, NaOH (2 M) solutions were added dropwise into the mixture with continuous stirring to adjust the pH value of 12.The suspension formed was transferred into Teflonlined stainless autoclave.The autoclave was sealed and maintained at 180°C for 3 h.Then, the autoclave was cooled naturally to room temperature and the resulting products were collected, washed with distillated water, and dried at 70°C for 2 h.NiFe 2 O 4 nanoparticles obtained in this stage were used to prepare the ZnO/NiFe 2 O 4 nanocomposites.

Synthesis of ZnO-NiFe 2 O 4 nanocomposites
The nanocomposites of ZnO-NiFe 2 O 4 were synthesized by simple solvothermal method.In typical synthesis Zn(NO 3 ) 2 .4H 2 O and NiFe 2 O 4 nanoparticles were dissolved in 40 mL ethanol and then mixed under magnetic stirring for 30 min.The subsequent procedures as similar to the synthesis of NiFe 2 O 4 nanoparticles.In order to study the effect of amount of NiFe 2 O 4 on the photocatalytic activity of ZnO/ NiFe 2 O 4 nanocomposites, a series of ZnO/NiFe 2 O 4 with different NiFe 2 O 4 amount were synthesized.The obtained products with different ZnO:NiFe 2 O 4 mole ratio value 1: 0.01, 1:0.05, and 1:0.1 were labeled as NNi1, NNi2, and NNi3, respectively.In addition, the variation of reaction temperatures on the heating suspension in autoclave were done only for NNi1.The temperature were 160, 180, and 200°C for the NN1-160, NN1-180, and NN1-200, respectively.For comparison purposes, the same procedure was used for the preparation of ZnO using zinc nitric as initial material.

Characterization
The structures of synthesized samples were studied by X-ray diffraction (XRD; XPERT-PRO Diffractometer system).The surface morphology and composition of samples were scanned using field emission scanning electron microscopy equipped with an energy dispersive X-ray spectrometer (FESEM-EDXS; FEI Inspect F50) and transmission electron microscopy (TEM, JEM-1400).Magnetic properties of synthesized samples were measured by a vibrating sampler magnetometer (VSM; OXFORD VSM 1.2H).Diffuse reflectance spectrophotometer UV-vis (Shimadzu UV-vis 2450 spectrophotometer) was used to record the absorbance spectra of samples at room temperature.The interaction in nanocomposites was investigated by Fourier transform infrared spectroscopy (FTIR Thermo Nicolet iS5).Thermogravimetry (TG) of NNi1 nanocomposite was recorded at a heating rate of 10 °/min using a thermogravimetric analyzer (LECO TGA 701).

Evaluation of photocatalytic activity
Photocatalytic activity of nanocomposites was evaluated by degradation of Rhodamine B (Rd B) under ambient atmospheric conditions using solar light irradiation.The procedure was adopted from the previous work 24 .For each experiment, 0.015 g of photocatalyst was dispersed in 20 mL of Rd B dye (10 mg/L) in aqueous solution.The mixture was kept under solar light irradiation and 5 mL samples were taken after irradiated for 1, 2 and 3 h (from 11: 00 am to 14: 00 pm).The progress of photocatalytic degradation of Rd B was monitored by measuring the absorbance in UV-vis spectrophotometer at the wave length of 553 nm.The influence of the loading amount of catalyst, reaction temperature, and the length of exposure time on the photodegradation process were investigated.The reusability of photocatalysts were carried out by collected the nanoparticles after first reaction cycles, and then evaluated as same as fresh sample.For comparison purposes the same procedure was also performed on ZnO and NiFe 2 O 4 .Degradation percentage of Rd B was calculated according to follow equation, degradation (%) = (A 0 -A)/A 0 x100% 25 .

Structural studies
Fig. 1 shows the XRD patterns of the ZnO, NiFe

Morphology and composition
The morphology and elements composition NN1-180 and NN1-200 were analyzed by FESEM-EDS and more over for NN 1 -200 the morphology was also analyzed by TEM.All the images for both techniques analysis are illustrated in Fig 2 .The morphology of NNi 1 -180 (Fig. 2a) show the granularlike shape with small agglomeration, meanwhile, the NNi1-200°C (Fig. 2b) have regularly shape lead to rod-like formation.Furthermore, the TEM image in Fig. 2c illustrates clearly the NNi 1 shape with rodlike particles which was synthesized at 200°C.The rod-like particles of NN 1 -200 have average of 40 nm and 200 nm in width and length, respectively.From these resuts can be concluded that the increase of temperature affects the formation and size of particles.As reported by Zhu et.al. 26 , the shape of ZnO particles easily changed with a change in temperature and the reaction conditions.The EDS spectra of NNi1 composition elements are shown in Fig. 2d.In this spectra can be observed the peaks of Zn Ni, Fe and O elements with a percentage of 86.06, 0.70, 1.50 and 11.74%, respectively.These results indicate that NiFe 2 O 4 particles have been coupled with ZnO.

Magnetic properties analysis
Fig. 3. shows the magnetic histeresys loops of NNi 1 , NNi 2 , and NNi 3 measured by vibrating sample magnetometer (VSM).The saturation magnetization (Ms) value of these nanocomposites increase gradually with the increasing amount of NiFe 2 O 4 , which is 1.04 emu/g, 4.32 emu/g, and 8.77 emu/g for NNi 1 , NNi 2 , and NNi 3 , respectively.These values indicate superparamagnetic properties.It is well known that ZnO is diamagnetic 27 , while synthesized NiFe 2 O 4 nanoparticles in this work are typical ferromagnetics with the Ms of 52.8 emu/g which is higher than Ms value reported for NiFe 2 O 4 earlier by the another authors [28][29][30] .Appearance superparamagnetic properties in nanocomposites

Optical properties analysis
UV-vis DRS was used to investigate the optical properties of the samples.Fig. 4. gives the UV-vis DRS spectra of NiFe 2 O 4 , ZnO, and NNi1.The results show that NiFe 2 O 4 nanoparticles have a good ability to absorb light in the visible area due to the small band gap of NiFe 2 O 4 , however this nanoparticle is rarely applied as a visible light photocatalyst alone since the electrons could not survive long in the conduction band and it will return to the valence band (h + ).Consequently photodegradation processes do not take place as it should 19 .Otherwise, pure ZnO absorbs strongly in the UV light area (below 400 nm) and weakly in visible light area.Combining both of NiFe 2 O 4 and ZnO can enhance absorptive capacity in the visible light region and can be applied for photocatalytic processes under solar light.The band gap (Eg) of NiFe 2 O 4 , ZnO and NNi1 are 1.64, 3.12, and 2.78 eV, respectively which were determined by Eg=1240/l equation 31 .

TG Analysis
Thermal stability of NNi1 nanocomposite sample was analyzed by TGA technique as shown in Fig. 5.There are two steps weight loss of sample by increasing the temperature.First step, the weight loss of 2% around 100°C is due to the evaporation of absorbed water in the powders.The second one is the weight loss in the area around 200-300°C predicted as organic residues that remaining in the sample with the weight loss of 4%.The temperature

Time (h)
0.005 g 0.010 g 0.015 g 0.020 g along 400 to 1000°C there is no significant weight loss occurred.In conclusion the weight losses of 6% on the whole could be said the sample having thermal stability under this temperature.

FTIR Analysis
Interaction between NiFe 2 O 4 and ZnO in nanocomposites was studied by the FTIR spectra as illustrated in Fig. 6.The FTIR spectra of nanocomposite show a sharp peak in the area around 500 cm -1 which is the characteristic peaks for Zn-O vibration, while the combination of ferrite and ZnO peaks seen in the area around 601 cm -1 .The broad peak located at 3500 cm -1 corresponds to the O-H vibration of absorbed water.In the spectra of synthesized NiFe 2 O 4 is observed a sharp peak at 601 cm -1 to vibration intrinsic of tetrahedral site and at 417 cm -1 to the octahedral vibration.As reported by previous researchers that based on the geometrical configuration of the oxygen nearest neighbors the metal ions are situated in two different sublattices, which are tetrahedral and octahedral in ferrites.The vibrational spectra of ferrite with a high frequency in the region of 610-580 cm -1 to the intrinsic vibration of tetrahedral and lower frequency in the region of 440-400 to octahedral site 23 .

Photocatalytic activity
The photocatalytic activity of the samples was evaluated by the degradation of Rd B as an example of dye under solar light irradiation as shown in Fig. 7.It is found that without photocatalysts the degradation percentage of Rd B is 19% for 3h.In the presence of NiFe 2 O 4 , there is not significant increase of the Rd B degradation.However, the degradation of Rd B was rapidly increasing with as the addition of any catalysts.From Fig. 7a, Rd B was degraded around 99, 96 and 92% for 3 h in the presence of NNi 1 , NNi 2 and NNi 3 , respectively.The pure ZnO shows activity in photodegradation of Rd B with the degradation in solution is 68% for 3 h.These results indicate that the photocatalytic activity of nanocomposites were higher than ZnO and NiFe 2 O 4 .The most excellent photocatalytic activity under solar light irradiation was performed by NNi 1 which is 99% of degration for 3 h.These results are in agreement with the DR-Uv-vis analysis given in Fig. 4 in which the absorption area for NNi 1 samples are shift into visible light consequently applicable under visible light region of the sun.
The mechanism of increase the degradation percentage of Rd B in the presence of synthesized nanocomposites can be described as follows: under solar light irradiation the electrons in valence band (CB) of NiFe 2 O 4 and ZnO will be excited to the conduction band (CB) separately, leaving holes with positive charge in VB.The difference of band between NiFe 2 O 4 and ZnO will facilitate the photogenerated electrons transfer from the CB of NiFe 2 O 4 to the CB of ZnO and the holes move from the VB of ZnO to the VB of NiFe 2 O 4, respectively.After that, the generated electrons react with O 2 contained in solution to yield O 2 -ions will further react with H 2 O, forming OH .hydroxyl radical.Hydroxyl radical is a very active group that will attack the compounds in the Rd B to be the simple compounds such as CO 2 and H 2 O 11 .
The photocatalytic activities of the sample NNi 1 -160, NNi1-180, and NNi 1 -200 on degradation of Rd B can be seen in Fig 8a .The best photocatalytic activities is shown by NNi 1 -200 due to the composite particle shape more regular and there is no agglomeration as shown in SEM and TEM image (Fig. 2).The increase in reaction temperature on the synthesis of NNi1 influences the morphology and size of nanocomposite particles and it is affect on photocatalytic activity.The uniform particle shape and size of nanocomposite is estimated to improve the photocatalytic activity.
From economic viewpoint, catalyst loading is an important parameter in heterogeneous photocatalysis reaction.In order to determine the effect of catalyst loading on photodegradation of Rd B, the experiment were carried out by increasing catalyst loading of NNi 1 from 0.005 to 0.02 g (Fig. 8b).The degradation percentage of Rd B increased as catalyst loading increasing.After 3 h irradiation, Rd B degradation percentage by catalyst loading of 0.015 mg give almost the same value with 0.02 g, which are 99.1 and 99.4%, respectively.These mean the catalyst loading maximum for degradation of Rd B is 0.015 g in 20 mL solution (10 mg/L).It surely these materials are potential if used as a photocatalyst to degrade dye in water.
The reaction kinetic of photocatalytic degradation of Rd B was also studied and the  22 .The apparent rate constant of NNi 1 (k) is 0.025375 min -1 and the correlation constant for the fitted lines were calculated to be R 2 = 0.9903.
In order to evaluate the photostability and reusability of nanocomposite, five recycling test for degradation of Rd B under solar light have been conducted only for NNi 1 (Fig 9b).The nanoparticles of NNi 1 were collected by filtered, washed with distillated water and then dried at 100°C for one hour.It is clearly seen that recycled NNi 1 still have good activity for Rd B degradation after five cycles, indicating the photostability of these catalysts.The degradation percentage decreased insignificantly and this result shows the reusability of NNi 1 as photocatalyst is promising.

CONCLUSION
In this present study, we have successfully synthesized magnetic nanocomposite photocatalysts of ZnO-NiFe 2 O 4 by simple solvothermal method using nitric salts as star ting materials and ethanol as solvent.The structural and elemental analysis confirmed the formation of ZnO-NiFe 2 O 4 nanocomposites and the specific ratios of Zn, Ni, Fe and O.The microstructure studies revealed that nanocomposites were dominated by granular-like of ZnO nanoparticles that synthesized at 180 °C and rod-like at 200°C.The estimated band gap value of ZnO-NiFe 2 O 4 (1:0.01)nanocomposites is 2.78 eV which is lower than ZnO.The magnetic saturation (Ms) result showed a ferromagnetic behavior of NiFe 2 O 4 and superparamagnetic of ZnO-NiFe 2 O 4 .The photocatalytic activity of all nanocomposites were higher than ZnO and NiFe 2 O 4 and the most excellent photocatalytic activity under solar light irradiation was performed by nanocomposite with the molar ratio of ZnO:NiFe 2 O 4 was 1:0.01 which 99% of Rd B was degradated after irradiated for 3 h.Hence, this nanocomposite is very potential if it used for degradation of dyes under solar light and then can be separated from the liquid using external magnetic field to be used in the subsequent photocatalytic processes.

Fig. 9 :
Fig. 9: (a) Plot ln C 0 /C vs irradiation time for degradation of Rd B using NNi 1 as catalyst and (b) 5 recycling experiments of NNi 1 for Rd B degradation (initial Rd B 10 mg/L; catalyst dosage: 0.015 g; 20 mL Rd B solutions) with strong magnetic materials like spinal ferrites of CoFe 2 O 4 , MgFe 2 O 4 , ZnFe 2 O 4, and CaFe 2 O 4