Biosynthesis of MgFe2O4 magnetic nanoparticles and its application in photo-degradation of malachite green dye and kinetic study

Document Type: Research Paper

Authors

Department of Chemistry, University of Zanjan, Zanjan, Iran

Abstract

In this study, we have reported the green synthesis magnesium ferrite using tragacanth gel by the sol-gel method without using any organic chemicals. The sample was characterized by powder X-ray diffraction (XRD), Fourier Transform Infrared Spectroscopy (FTIR), vibrating sample magnetometer (VSM) and scanning electron microscopy (SEM). The X-ray powder diffraction (XRD) analysis revealed the formation of cubic phase ferrite MNPs. Magnetic analysis showed that the MgFe2O4 had a superparamagnetic behavior with a saturation magnetization of 14 emu/g at room temperature. The present catalyst displays high photocatalytic activity for the removal of malachite green dye under irradiation with visible light. The effects of MgFe2O4 dosage, initial dye concentration and visible light irradiation on dye degradation were evaluated. The results demonstrated that the catalyst can degrade ca. 98% of the malachite green dye. The catalyst can be easily recovered by a simple magnetic separation and can be recycled six times with no significant loss of photocatalytic activity.

Keywords


INTRODUCTION

Spinel ferrites have achieved huge attention in recent years because of their useful electrical and magnetic properties. Spinel ferrites have different applications in information storage systems, permanent magnets, sensors, magnetic drug delivery, recording heads, antenna rods, catalysis, loading coils, magnetic liquids, telecommunication devices, magnetic refrigeration, and as a microwave absorber [1-7]. So much interest has been paid on the synthesis and characterization of nanoparticles of spinel ferrites. Molecular formula of magnetic spinel ferrites is MFe2O4 in which M can be any divalent metal cation. In spinel ferrite, M2+ and Fe3+ occupy the tetrahedral (A) and octahedral (B) interstitial sites of the fcc lattice formed by O2− ions, respectively [8-12]. The unit cell of a spinel ferrite consists of 32 oxygen atoms, 16 trivalent irons and 8 divalent metal ions [13, 14].

Magnesium ferrite (MgFe2O4) is one of the important spinels with a cubic structure of the normal spinel-type. These nanoparticles have a band gap of 2.18 eV, so their magnetic NPs could be potential photocatalytic to remove the pollution [15, 16]. There are various chemical and physical methods for the synthesis of nanoparticles such as sol-gel methods [2,17-18], sonochemical technique [19], hydrothermal methods [20, 21], microwave processing approaches [22], co-precipitation [23, 24], etc. The use of natural gels in the synthesis of nanoparticles has attracted the attention of researchers, due to the lack of toxicity, cost-effectiveness and environmental compatibility [25-27].

Lately, various methods, such as coagulation, advanced oxidation processes (AOP), electrochemical, ozonation, sonolysis, and photocatalysis, have been applied in the removal of organic dyes and industrial pollutants [28-31]. Among all the methods, advanced oxidation processes by heterogeneous photocatalysis have been considered for removal of contaminants [32-34]. Malachite green (MG) (Fig. 1) is a cationic triphenylmethane dye which is usually used in the laboratory, coloring agents in leather, food, textile, tannery, plastic, wool, etc. Malachite green is not easily degradable, it is mutagenic and carcinogenic [35, 36]. In this study, we have reported, the synthesis of superparamagnetic magnesium ferrite nanoparticles using TG by the sol-gel method as a cheap, facile and friendly approach to the nature. The photocatalytic activity of magnesium ferrite nanoparticles has been assessed for the removal of MG dye. The magnesium ferrite nanoparticles demonstrated the highest catalytic properties for the degradation of MG in short time.

EXPERIMENTS

Materials

The Tragacanth gum (TG) was obtained from a local health food store. All the chemicals were purchased from Merck and daijung (Darmstadt, Korea), and used without further purification. Phase identification of MgFe2OMNPs was characterized by X-ray powder diffraction (XRD) with a X’Pert PRO advanced diffractometer using Cu (Kα) radiation (wavelength: 1.5406 Å) in the range of 2θ from 10 to 80. The morphological properties of the sample were studied by using scanning electron microscope (Zeiss EVO 18, Germany). Optical properties was assessed by a double beam UV-Vis absorption spectrophotometer (Analytical Jena-Specord 205, Germany). The infrared spectra (FTIR, Mattson, Unicam Ltd., Cambridge, UK) and vibrating sample magnetometer (VSM, Meghnatis Kavir Kashan Co., Kashan, Iran) were used to detect functional groups and investigate magnetic properties of the sample, respectively.

Preparation of MgFe2OMNPs

In the first step, 40 ml of deionized water was poured into a beaker and then 0.2 g of tragacanth gum (TG) was added to deionized water and stirred for 80 minutes at 70°C to obtain a clear TG solution. After that, 1mmol of Mg (NO3)2.6H2O and 2mmol of Fe (NO3)3. 9H2O were added to the TG solution. The beaker was placed in a sand bath at 75C with continuous stirring until the formation of dry gel. Finally, the dry gel was calcined at 600C for four hours.

Photocatalytic dye degradation

Experiments were carried out in a batch mode photoreactor. The irradiation source was a fluorescent lamp (λ> 400 nm, 80 W, Parmis, Iran)placed above the batch photoreactor. The photocatalytic dye degradation experiment was conducted by various amounts of MgFe2O4 (0.005, 0.01, 0.015 and 0.02 g) in photoreactor containing 50 mL of a dye solution (20 mg/L) at room temperature. The effect of initial dye concentration on the photodegradation of dyes was investigated. The MgFe2O4 (0.015 g) was added to 50 mL of various dye concentrations (5, 10, 15 and 20 mg/ L). The effect of visible light irradiation on the removal of dyes was surveyed. The MgFe2O4 MNPs were separated from the solution applying a magnet, and the alteration on the absorbance at a λmax of MG dye (619 nm) was checked by UV–Vis spectrophotometer. The degradation percentage of dye was calculated from the following equation

 

Wwhere A0 is the initial absorbance and At is the absorbance at the time t.

The removal of MG follows the pseudo-first order kinetics and the rate constant is determined by the following relation:

 

The rate constant k is calculated from the slope of straight line portion of ln (C0/Ct) versus t plot.

RESULTS AND DISCUSSION

Characterization of MgFe2O4 nanoparticles

Fig. 2a shows the IR spectrum of the sample calcined at 600°C for 4 hours. According to Fig. 2a, two strong absorption bands ν1 and ν2 are observed at 612 cm−1 and 421 cm−1, respectively. The difference between ν1 and ν2 is due to the changes in bond length (Fe-O) at the octahedral and tetrahedral sites. The bands at 3400 cm−1 and 1630 cm−1 are characteristic for hydroxyl group (O-H) [15].

The XRD pattern of the sample is shown in Fig. 2b. XRD analysis displayed a series of diffraction peaks at 2θ of 30.35, 35.78, 37.11, 43.35, 53.71, 57.28, 62.87 and 74.10 which can be assigned to (220), (311), (400), (422), (511), (440) and (533) planes, respectively. All the diffraction peaks were readily indexed to a pure cubic structure ferrite (JSPDS Card no. 73-2211) with a=b=c= 8.363 Å. The average crystallite size of sample was calculated from the full width at half maximum (FWHM) of the XRD patterns using the well- known Scherrer formula: D = 0.9λ/β cosθ,

Wwhere D is the crystallite size (nm), β is the full width at half maximum of the peak, λ is the X-ray wavelength of Cu Kα= 0.154 nm and θ is the Bragg angle [37]. Based on the Scherer formula, the average crystallite size of MgFe2OMNPs was calculated to be about 11 nm.

The SEM image shows the particle size and external morphology of the ferrite nanoparticles that calcined at 600ºC for 4h (Fig. 2c). It can be seen from the SEM image that the ferrite nanoparticles have fairly uniform spherical shape and narrow size distributions.

The magnetic attributes of MgFe2O4-NPs have been investigated by using vibrating sample magnetometer (VSM). Magnetization curve shows superparamagnetic properties which means magnetic remanence (Mr) and coercive force (Hc) are zero. As can be observed in Fig. 2d, the specific saturation magnetization value was measured to be 14 emu/g for MgFe2O4-NPs. The prepared MgFe2O4 MNPs, were studied as a catalyst for removal of the MG dye with visible light irradiation and air at room temperature.

Effect of visible light irradiation and MgFe2O4 MNPs catalyst

Removal of MG dye was evaluated with visible light irradiation only, and catalyst under both visible light irradiation and dark. In the first case, without any catalyst, we had maximum degradation of 9%, while using magnetic magnesium ferrite catalyst without visible light irradiation, we had no degradation. As shown in Fig. 3, in the presence of both catalyst and light, 98% of MG dye is degraded at the irradiation time of 60 min.

Effect of photocatalyst dosage

Fig. 4 displays the decolorization efficiency at various concentrations of catalyst (0.005, 0.01, 0.015 and 0.02 gr) at 50 ml of MG dye. The experiments were done by the catalyst at a fixed dye concentration, 20 mg/L of at 60 minutes of irradiation. Experimental results show a trend of reduced removal with increasing magnesium ferrite concentration. Heterogeneous photocatalytic reactions are well known to exhibit an adequate increase in photodegradation with catalyst loading [38]. Generally, in any given photocatalytic application, the optimum catalyst concentration must be determined, in order to avoid excess catalyst and ensure total absorption of efficient photons [39]. Fig. 4 suggests that the initial rate of decolorization may increase linearly up to about 0.0.015 g magnesium ferrite.

Effect of Initial Dye Concentration

Removal of MG dye by visible irradiation/MgFe2O4 process was studied by varying the initial concentration of MG (5, 10, 15, 20 mg/L) at a constant MgFe2O4 dosage (0.015 g) (Fig. 5). The photocatalytic degradation of MG dye was not much decrease with increasing the initial dye concentration from 5 to 20 mg/L after 60 min.

Photodegredation of MG dye at different times

The photocatalytic activities of the as ‐synthesized magnetic MgFe2O4 photocatalyst for degradation of the MG were investigated in the presence of visible light irradiation and air at room temperature. The UV–visible spectra of MG aqueous solution in the presence of magnetic photocatalyst and air under visible light irradiation (λ > 400 nm) at room temperature for various time intervals are shown in Fig. 6. Obviously, the major absorption peak of MG is located at 619 nm which declines quickly with increasing exposure time and fully vanishes after irradiation for about 60 min. Almost 98% of MG can be degraded in 60 min. These results indicate that magnesium ferrite MNPs has a unique visible‐light photocatalytic activity for degradation of the organic dyes.

Kinetic studies

Most of the photodegradation reactions of pollutants obey first order reaction kinetics [40], where the relationship between degradation rate and irradiation time (t) can be described by ln(C0/Ct) = kt,

Wwhere k is the reaction rate constant. A plot of ln (C0/Ct) versus time represents a straight line; the slope equals the apparent first-order rate constant k. The kinetics of photodegradation of MG dye by MgFe2O4 nanoparticles were investigated and the results are revealed in Fig. 7. According to the slope of line (Fig. 7) the rate constant value for removal of MG dye was calculated to be k = 0.0636 min-1. Furthermore, the fitting correlation coefficient (R2) is calculated to be 0.989.

Reuse of the photocatalyst

The magnesium ferrite MNPs catalyst can be used repeatedly for the removal of dye solution. To measure the reusability of the catalyst, the removal of MG under visible light irradiation was investigated after gathering and reusing the same catalyst for subsequent runs. It can be seen from Fig. 8, the photocatalytic activity of the catalyst does not show any clear loss after six recycles for the photodegradation of MG, illustrating that the magnetic photocatalyst has good stability. Moreover, the MgFe2O4 MNPs is able to be separated from the reaction solution by a magnet after degradation. So, the magnetic photocatalyst is stable against photocorrosion during the degradation of organic dye.

Proposed mechanism for the photodegradation of dye in the presence of MgFe2O4 MNPs

A proposed mechanism for the photodegradation of malachite green dye in the presence of MgFe2O4 MNPs under visible light irradiation is demonstrated in Fig. 9. The valence band holes and their electron pair transfer to the surface, where they react with absorbed electron donors and electron acceptors (water, hydroxide ions) generating surface-bound hydroxyl radicals. The surface OH radicals can oxidize malachite green dye [34].

CONCLUSION

The biosynthesis of superparamagnetic magnesium ferrite nanoparticles using tragacanth gel (TG) by the sol-gel method is reported in this paper. A single phase with a cubic spinel structure was formed after heat treatment at 600°C for only 4 h. This method has many advantages such as nontoxic, economic viability, ease to scale up, less time consuming and environmentally friendly approach for the synthesis of MgFe2O4 nanoparticles without using any organic chemicals. The photocatalytic activity of magnesium ferrite nanoparticles has been evaluated for the degradation of malachite green dye in water under visible light irradiation. It was demonstrated that the catalyst could remove as high as 98% of the dye. The current photocatalyst could be removed from the reaction mixture with external magnet and its recyclability remains effective and active after six cycles.

CONFLICT OF INTEREST

The authors declare that there is no conflict of interests regarding the publication of this manuscript.

 

 

[1] Bahrami M, Ramazani A, Hanifehpour Y, Fattahi N, Taghavi Fardood S, Azimzadeh Asiabi P, et al. In situgenerated stabilized phosphorus ylides mediated a mild and efficient method for the preparation of some new sterically congested electron-poorN-vinylated heterocycles. Phosphorus, Sulfur, and Silicon and the Related Elements. 2016;191(10):1368-74.

[2] Taghavi Fardood S, Ramazani A, Joo SW. Eco-friendly synthesis of magnesium oxide nanoparticles using arabic Gum. J Appl Chem Res. 2018; 12(1): 8-15.

[3] Alizadeh N, Shariati S, Besharati N. Adsorption of Crystal Violet and Methylene Blue on Azolla and Fig Leaves Modified with Magnetite Iron Oxide Nanoparticles. International Journal of Environmental Research. 2017;11(2):197-206.

[4] Amoli Diva M, Pourghazi K. CoFe2O4 nanoparticles grafted multi-walled carbon nanotubes coupled with surfactant-enhanced spectrofluorimetry for determination of ofloxacin in human plasma. Nanochemistry Research. 2018; 3(1): 17-23.

[5] Ghotekar S, Pansambal S, Pagar K, Pardeshi O, Oza R. Synthesis of CeVO4 nanoparticles using sol-gel auto combustion method and their antifungal activity. Nanochemistry Research. 2018; 3(2): 189-96.

[6] Ramazani A, taghavi fardood s, Ebadzadeha B, Azimzadeh Asiabi P, Bigdeli Fard Y. Microwave-assisted multicomponent reaction for the synthesis of 2-amino-4H-chromene derivatives using ilmenite (FeTiO3) as a magnetic catalyst under solvent-free conditions. Asian Journal of Green Chemistry. 2017;1(Issue 1. pp. 1-55):34-40.

[7] TAGHAVI FS, Ramazani A, Golfar Z, WOO JS. Green Synthesis of α-Fe2O3 (hematite) Nanoparticles using Tragacanth Gel. 2017.

[8] Kooti M, Sedeh AN. Synthesis and Characterization of NiFe2O4 Magnetic Nanoparticles by Combustion Method. Journal of Materials Science & Technology. 2013;29(1):34-8.

[9] Ramazani A, Taghavi Fardood S, Hosseinzadeh Z, Sadri F, Joo SW. Green synthesis of magnetic copper ferrite nanoparticles using tragacanth gum as a biotemplate and their catalytic activity for the oxidation of alcohols. Iranian Journal of Catalysis. 2017; 7(3): 181-5.

[10] Rostami Z, Rouhanizadeh M, Nami N, Zareyee D. Fe3O4 magnetic nanoparticles (MNPs) as an effective catalyst for synthesis of indole derivatives. Nanochemistry Research. 2018; 3(2): 142-8.

[11] Atrak K, Ramazani A, Taghavi Fardood S. Green synthesis of Zn0.5Ni0.5AlFeO4 magnetic nanoparticles and investigation of their photocatalytic activity for degradation of reactive blue 21 dye. Environmental Technology. 2019:1-11.

[12] Sadri F, Ramazani A, Ahankar H, Taghavi Fardood S, Azimzadeh Asiabi P, Khoobi M, et al. Aqueous-phase oxidation of alcohols with green oxidants (Oxone and hydrogen peroxide) in the presence of MgFe2O4 magnetic nanoparticles as an efficient and reusable catalyst. Journal of Nanostructures. 2016; 6(4): 264-72.

[13] Atrak K, Ramazani A, Taghavi Fardood S. A novel sol–gel synthesis and characterization of MgFe2O4@γ–Al2O3 magnetic nanoparticles using tragacanth gel and its application as a magnetically separable photocatalyst for degradation of organic dyes under visible light. Journal of Materials Science: Materials in Electronics. 2018;29(8):6702-10.

[14] Moradnia F, Ramazani A, Taghavi Fardood S, Gouranlou F. A novel green synthesis and characterization of tetragonal-spinel MgMn2O4 nanoparticles by tragacanth gel and studies of its photocatalytic activity for degradation of reactive blue 21 dye under visible light. Materials Research Express. 2019;6(7):075057.

[15] Shahid M, Jingling L, Ali Z, Shakir I, Warsi MF, Parveen R, et al. Photocatalytic degradation of methylene blue on magnetically separable MgFe2O4 under visible light irradiation. Materials Chemistry and Physics. 2013;139(2-3):566-71.

[16] Su NR, Lv P, Li M, Zhang X, Li M, Niu J. Fabrication of MgFe2O4–ZnO heterojunction photocatalysts for application of organic pollutants. Materials Letters. 2014;122:201-4.

[17] Pradeep A, Priyadharsini P, Chandrasekaran G. Sol–gel route of synthesis of nanoparticles of MgFe2O4 and XRD, FTIR and VSM study. Journal of Magnetism and Magnetic Materials. 2008;320(21):2774-9.

[18] Taghavi Fardood S, Ramazani A, Joo SW. Sol-gel synthesis and characterization of zinc oxide nanoparticles using black tea extract. Journal of Applied Chemical Research. 2017; 11(4): 8-17.

[19] Chen D, Li D-y, zhang Y-z, Kang Z-t. Preparation of magnesium ferrite nanoparticles by ultrasonic wave-assisted aqueous solution ball milling. Ultrasonics Sonochemistry. 2013;20(6):1337-40.

[20] Verma S, Joy PA, Khollam YB, Potdar HS, Deshpande SB. Synthesis of nanosized MgFe2O4 powders by microwave hydrothermal method. Materials Letters. 2004;58(6):1092-5.

[21] Singh R, Kumar M, Tashi L, Khajuria H, Sheikh HN. Hydrothermal synthesis of nitrogen doped graphene supported cobalt ferrite (NG@CoFe2O4) as photocatalyst for the methylene blue dye degradation. Nanochemistry Research. 2018; 3(2): 149-59.

[22] Chen D, Zhang Y, Tu C. Preparation of high saturation magnetic MgFe2O4 nanoparticles by microwave-assisted ball milling. Materials Letters. 2012;82:10-2.

[23] Hankare PP, Jadhav SD, Sankpal UB, Patil RP, Sasikala R, Mulla IS. Gas sensing properties of magnesium ferrite prepared by co-precipitation method. Journal of Alloys and Compounds. 2009;488(1):270-2.

[24] Saeidian H, Moradnia F. Benign synthesis of N-aryl-3,10-dihydroacridin-1(2H)-one derivatives via ZnO nanoparticle-catalyzed Knoevenagel condensation/intramolecular enamination reaction. Iranian Chemical Communication. 2017; 5(Issue 3, pp. 237-363): 252-61.

[25] Otari SV, Patil RM, Nadaf NH, Ghosh SJ, Pawar SH. Green synthesis of silver nanoparticles by microorganism using organic pollutant: its antimicrobial and catalytic application. Environmental Science and Pollution Research. 2013;21(2):1503-13.

[26] Sorbiun M, Shayegan Mehr E, Ramazani A, Mashhadi Malekzadeh A. Biosynthesis of metallic nanoparticles using plant extracts and evaluation of their antibacterial properties. Nanochemistry Research. 2018; 3(1): 1-16.

[27] Taghavi Fardood S, Moradnia F, Ramazani A. Green synthesis and characterisation of ZnMn2O4 nanoparticles for photocatalytic degradation of Congo red dye and kinetic study. Micro & Nano Letters. 2019;14(9):986-91.

[28] Atrak K, Ramazani A, Taghavi Fardood S. Eco-friendly synthesis of Mg0.5Ni0.5AlxFe2-xO4 magnetic nanoparticles and study of their photocatalytic activity for degradation of direct blue 129 dye. Journal of Photochemistry and Photobiology A: Chemistry. 2019;382:111942.

[29] Majidi R, Parhizkar J, Karamian E. Photocatalytic Removal of NOx Gas from Air by TiO2/Polymer Composite Nanofibers. Nanochemistry Research. 2018; 3(2): 212-8.

[30] Chamack M, Mahjoub A, Hosseinian A. Facile Synthesis of Nanosized MgO as Adsorbent for Removal of Congored Dye from Wastewate. Nanochemistry Research. 2018; 3(1): 85-91.

[31] Ouni L, Ramazani A, Taghavi Fardood S. An overview of carbon nanotubes role in heavy metals removal from wastewater. Frontiers of Chemical Science and Engineering. 2019;13(2):274-95.

[32] Somasekhar R, Nookaraju M. Nanotitania composite assembled with Graphene oxide for Photocatalytic degradation of Eosin Yellow under Visible light. Nanochemistry Research. 2018; 3(2): 160-9.

[33] Amini M, Ashrafi M. Photocatalytic degradation of some organic dyes under solar light irradiation using TiO2 and ZnO nanoparticles. Nanochemistry Research. 2016; 1(1): 79-86.

[34] Moradi S, Taghavi Fardood S, Ramazani A. Green synthesis and characterization of magnetic NiFe2O4@ZnO nanocomposite and its application for photocatalytic degradation of organic dyes. Journal of Materials Science: Materials in Electronics. 2018;29(16):14151-60.

[35] Hameed BH, Lee TW. Degradation of malachite green in aqueous solution by Fenton process. Journal of Hazardous Materials. 2009;164(2-3):468-72.

[36] Wang X, Ni J, Pang S, Li Y. Removal of malachite green from aqueous solutions by electrocoagulation/peanut shell adsorption coupling in a batch system. Water Science and Technology. 2017;75(8):1830-8.

[37] Batoo KM, Kumar S, Lee CG, Alimuddin. Influence of Al doping on electrical properties of Ni–Cd nano ferrites. Current Applied Physics. 2009;9(4):826-32.

[38] Krýsa J, Keppert M, Jirkovský Jr, Štengl V, Šubrt J. The effect of thermal treatment on the properties of TiO2 photocatalyst. Materials Chemistry and Physics. 2004;86(2-3):333-9.

[39] Saquib M. TiO2-mediated photocatalytic degradation of a triphenylmethane dye (gentian violet), in aqueous suspensions. Dyes and Pigments. 2003;56(1):37-49.

[40] Rana N, Chand S, Gathania AK. Synthesis and characterization of flower-like ZnO structures and their applications in photocatalytic degradation of Rhodamine B dye. Journal of Materials Science: Materials in Electronics. 2015;27(3):2504-10.