- Nano Express
- Open Access
Efficient solar photocatalyst based on cobalt oxide/iron oxide composite nanofibers for the detoxification of organic pollutants
© Asif et al.; licensee Springer. 2014
- Received: 12 June 2014
- Accepted: 11 July 2014
- Published: 18 September 2014
A Co3O4/Fe2O3 composite nanofiber-based solar photocatalyst has been prepared, and its catalytic performance was evaluated by degrading acridine orange (AO) and brilliant cresyl blue (BCB) beneath solar light. The morphological and physiochemical structure of the synthesized solar photocatalyst was characterized by X-ray diffraction (XRD), field emission scanning electron microscopy (FESEM), X-ray photoelectron spectroscopy (XPS), and Fourier transform infrared spectroscopy (FTIR). FESEM indicates that the Co3O4/Fe2O3 composite has fiber-like nanostructures with an average diameter of approximately 20 nm. These nanofibers are made of aggregated nanoparticles having approximately 8.0 nm of average diameter. The optical properties were examined by UV-visible spectrophotometry, and the band gap of the solar photocatalyst was found to be 2.12 eV. The as-grown solar photocatalyst exhibited high catalytic degradation in a short time by applying to degrade AO and BCB. The pH had an effect on the catalytic performance of the as-grown solar photocatalyst, and it was found that the synthesized solar photocatalyst is more efficient at high pH. The kinetics study of both AO and BCB degradation indicates that the as-grown nanocatalyst would be a talented and efficient solar photocatalyst for the removal of hazardous and toxic organic materials.
- Acridine orange
- Brilliant cresyl blue
- Organic pollutant
- Solar photocatalyst
Recent industrial progress not only has positive consequences on human life but also causes big environmental threats due to the continuous release of industrial pollutants [1–3]. These pollutants cause too many serious problems for human and aquatic life because they are carcinogenic at trace levels for aquatic and non-aquatic environment [4–8]. Therefore, environmental pollution due to different types of pollutants created a center of global attention for the detoxification of these pollutants. A large number of physical, chemical, and biological methods were developed for water treatment but gained less importance because of low efficiency, high cost, and time consumption [9, 10].
Among various techniques, photocatalysis in the presence of heterogeneous photocatalysts is considered as a cheap, easy, and efficient method for the decomposition of risky pollutants to final non-toxic products [11–15]. However, this technique is mainly depending on the photocatalyst which is mostly utilized for photocatalysis. TiO2 is the most active catalyst among them used so far . Similarly, ZnO has also proven itself as one of the most active photocatalysts . However TiO2, ZnO, and other similar photocatalysts can only degrade organic pollutants under UV light due to their large band gap, and thus, activation of these photocatalysts can only be carried out under UV light irradiation [15, 16]. Therefore, utilization of these photocatalysts at a broad scale will result in small photoelectronic transition efficiency since the ultraviolet light comprises only 4% to 5% of the solar spectrum . Therefore, based on energy conservation and environmental pollution concerns, there is a need to develop visible light-driven photocatalysts with enhanced efficiency.
Doped and composite nanostructure metal oxides have been considered as interesting materials and have shown excellent properties in photocatalysis [1, 18]. Doping of nanomaterials modifies their features and characteristics. Nanocomposites generally increase numerous properties of metal oxide to fulfill the growing demand for various applications [19, 20]. Semiconductors are the potential host material for transition materials and have attracted great attention due to their outstanding performance and multidimensional applications. Doping and nanocomposition improve the surface area and reduce the size of the metal oxide nanostructure. Doping of nanomaterials also tunes the band gap energy and enhances the conductivity, electrical, mechanical, barrier, sensing, and solar photocatalytic properties [21, 22].
Cobalt oxide (Co3O4) nanomaterials have shown much application in different sectors. They have been used in Li-ion battery, catalysis, and sensing applications. All these properties depend on the particle size of Co3O4[23, 24]. Similarly, Fe2O3 has been used in sensing and photocatalysis. However, the main drawback related to this metal oxide is its photocatalysis in the presence of UV . Since cobalt oxide has oxidation catalysis and Fe2O3 has photocatalysis properties, the composite of these two oxides would probably show some interesting visible photocatalytic properties.
Therefore, in this research, a solar photocatalyst based on Co3O4/Fe2O3 composite nanofibers has been synthesized by an eco-friendly process and characterized by field emission scanning electron microscopy (FESEM), X-ray diffraction (XRD), X-ray photoelectron spectroscopy (XPS), Fourier transform infrared spectroscopy (FTIR), and UV-visible spectrophotometry. The catalytic properties of the as-grown solar photocatalyst were studied by degrading acridine orange (AO) and brilliant cresyl blue (BCB) at different pH under solar light.
Analytical reagent grade ferric nitrate nonahydrate Fe(NO3)3 · 9H2O, cobaltous nitrate hexahydrate Co(NO3)2 · 6H2O, sodium hydroxide NaOH, 99% ethanol C2H5OH, and other all chemicals were purchased from Sigma Aldrich (St. Louis, MO, USA).
Synthesis and mechanism of Co3O4/Fe2O3 composite nanofibers
The required amount for 0.1 M aqueous solutions of Fe(NO3)3 · 9H2O and 0.2 M of Co(NO3)2 · 6H2O was accurately weighed. Then, both the salts were completely dissolved together in 100 mL distilled water at ambient temperature, and the homogeneous solution's pH was adjusted up to 11.0 by dropwise addition of freshly prepared 0.2 M NaOH solution under constant and vigorous stirring. After that, the solution was heated at about 60°C to 70°C with constant stirring overnight. After heating, the solution was allowed to cool at ambient temperature and centrifuged to separate the precipitate at 2,000 rpm. The supernatant solution was discarded, and the precipitate was washed thrice with ethanol. The precipitate was dried in an oven at 50°C to 60°C, ground, and stored in a clean, dry, and inert plastic vial.
Growth mechanism of Co3O4/Fe2O3 composite nanofibers
The surface morphology of the nanoparticles was examined utilizing a JEOL scanning electron microscope (JSM-7600F, Akishima-shi, Japan). XRD patterns were obtained with a computer-controlled PANalytical X'Pert Explorer diffractometer (Almelo, The Netherlands). FTIR spectra were recorded in the range of 400 to 4,000 cm−1 on a PerkinElmer (Spectrum 100) FTIR spectrometer (Waltham, MA, USA). The UV spectrum was recorded from 200 to 800 nm using a UV-visible spectrophotometer (UV-2960, Labomed, Inc., Los Angeles, CA, USA).
Photocatalytic degradation of dye
The photocatalytic property of the composite nanofibers was evaluated by using toxic dyes AO and BCB under solar light, which is relatively stable in the absence of a nanomaterial. This photocatalytic degradation of fluorescent cationic dye was evaluated taking two different 100.0 mL, 1E10 − 4 M transparent solutions of dye in a large surface area vessel, e.g., beakers. These solutions were then adjusted to different pH, 7.0 and 10.0. Sodium hydroxide (0.2 M) was used to adjust the pH under vigorous and continuous stirring. Then, exactly weighed 0.1 g (up to 1 mg) of nanomaterial was added into both solutions, and the solutions were kept in the dark to provide equilibration time for physical adsorption phenomenon of the material onto the dye surface. These solutions were simultaneously irradiated by sun daylight with continuous stirring. All three experiments were performed under sunlight. After that, an aliquot of 4 to 5 mL were pipetted out from each solution after regular pattern of irradiation and centrifuged, and the absorbance of the transparent solution at a wavelength maximum of 483.0 nm was measured by using a spectrophotometer (Labomed, Inc.). The same experiment was also performed in the absence of a photocatalyst to find out the control decolorization of dye.
Physiochemical characterization of Co3O4/Fe2O3 composite nanofibers
Morphology study (FESEM)
Phase and compositional study (XRD)
The functional groups of the composite nanofibers were examined by FTIR as shown in Figure 2b. FTIR exhibited a peak for M-O-M stretching at 640 cm−1 along with some additional peaks for carbonate (1,341 cm−1) and water bending (1,632 cm−1) and stretching (3,361 cm−1). FTIR data suggests that the composite nanofibers are metal oxide-based nanostructures [2, 3].
Photoabsorption properties and band gap energy
Effect of pH
Control experiments and photocatalysis reaction
Statistical analysis for the degradation process of dyes
Afterwards, in view of regression analysis, the graph of ln A/A° vs. time was plotted for the AO dye at pH 7.0 and 10.0 while for the BCB dye at pH 7.0. Figures 5d and 6c show that the best linear relation exists between ordinates and abscissa for AO and BCB dyes, respectively.
Kinetics study of dye
where C° is the initial concentration of dyes and C is the concentration at time t. By utilizing Equation 6, we determined the apparent rate constant from the slope of the graph of ln(C/C°), which corresponds to ln (A/A°) vs. irradiation interval.
Pseudo-first-order rate constant and t 1/2 for AO and BCB in the presence of the composite nanofibers
Rate of decolorization
1.5000E − 06
1.7700E − 06
0.6720E − 06
Pseudo-first-order rate constant and t 1/2 for AO and BCB in the absence of the composite nanofibers
Rate of decolorization
0.2710E − 06
0.0552E − 06
Proposed degradation mechanism
The basic mechanism of the degradation process is depending upon electron-hole (e-h) charge separation. Irradiation of visible light that corresponds to the band gap energy of the composite nanofibers leads the valence band electron to be excited to the conduction band while creating a hole in the valence band. This e- h charge separation initiates the radical-generated oxidation-reduction reaction of organic dyes.
These photogenerated electrons strike the surrounding oxygen and convert them into superoxide anion radicals (O2·−), which are further transformed into H2O2, followed by · OH radicals after reacting with H+ from water molecules. Similarly, the photogenerated hole in the valence band initializes the homolysis of water molecules and introduces · OH radicals which degrade the dye molecules.
Well-crystalline Co3O4/Fe2O3 composite nanofibers were prepared by a low-temperature process and examined by different spectroscopic techniques. The nanofibers were optically active and showed potential application as a solar photocatalyst by well-organized degradation of AO and BCB. Thus, it is concluded that nanofibers are an active photocatalyst for achieving capable photocatalysts in favor of water resources and health observation.
This paper was funded by the Deanship of Scientific Research (DSR), King Abdulaziz University, Jeddah, under Grant No. T-001/431. The authors, therefore, acknowledge with thanks DSR for the technical and financial support.
- Khan SB, Lee J-W, Marwani HM, Akhtar K, Asiri AM, Seo J, Khan AAP, Han H: Polybenzimidazole hybrid membranes as a selective adsorbent of mercury. Compos B 2014, 56: 392–396.View ArticleGoogle Scholar
- Khan SB, Faisal M, Rahman MM, Jamal A: Exploration of CeO2 nanoparticles as a chemi-sensor and photo-catalyst for environmental applications. Sci Tot Environ 2011, 409: 2987–2992. 10.1016/j.scitotenv.2011.04.019View ArticleGoogle Scholar
- Khan SB, Faisal M, Rahman MM, Jamal A: Low-temperature growth of ZnO nanoparticles: photocatalyst and acetone sensor. Talanta 2011, 85: 943–949. 10.1016/j.talanta.2011.05.003View ArticleGoogle Scholar
- Jain RK, Kapur M, Labana S, Lal B, Sharma PM, Bhattacharya D, Thakur IS: Microbial diversity: application of microorganisms for the biodegradation of xenobiotics. Curr Sci 2005, 89: 101–112.Google Scholar
- Lin W-C, Chen C-H, Tang H-Y, Hsiao Y-C, Pan JR, Hu C-C, Huang C: Electrochemical photocatalytic degradation of dye solution with a TiO2-coated stainless steel electrode prepared by electrophoretic deposition. Appl Catal B Environ 2013, 140–141: 32–41.View ArticleGoogle Scholar
- Nenavathu BP, Rao AVRK, Goyal A, Kapoor A, Dutta RK: Synthesis, characterization and enhanced photocatalytic degradation efficiency of Se doped ZnO nanoparticles using trypan blue as a model dye. Appl Catal A Gen 2013, 459: 106–113.View ArticleGoogle Scholar
- Chuang YH, Tzou YM, Wang MK, Liu CH, Chiang PN: Removal of 2-chlorophenol from aqueous solution by Mg/Al layered double hydroxide (LDH) and modified LDH. Ind Eng Chem Res 2008, 47: 3813–3819. 10.1021/ie071508eView ArticleGoogle Scholar
- Goharshadi EK, Hadadian M, Karimi M, Azizi-Toupkanloo H: Photocatalytic degradation of reactive black 5 azo dye by zinc sulfide quantum dots prepared by a sonochemical method. Mater Sci Semicond Proc 2013, 16: 1109–1116. 10.1016/j.mssp.2013.03.005View ArticleGoogle Scholar
- Yao Y, Huang Z, Zheng B, Zhu S, Lu W, Chen W, Chen H: Electrochemical photocatalytic degradation of dye solution with a TiO2-coated stainless steel electrode prepared by electrophoretic deposition. Curr Appl Phys 2013, 13: 1738–1742. 10.1016/j.cap.2013.07.006View ArticleGoogle Scholar
- Qin G, Sun Z, Wu Q, Lin L, Liang M, Xue S: Dye-sensitized TiO2 film with bifunctionalized zones for photocatalytic degradation of 4-cholophenol. J Hazard Mater 2011, 192: 599–604. 10.1016/j.jhazmat.2011.05.059View ArticleGoogle Scholar
- Xu R, Li J, Wang J, Wang X, Liu B, Wang B, Luan X, Zhang X: Photocatalytic degradation of organic dyes under solar light irradiation combined with Er3+: YAlO3/Fe- and Co-doped TiO2 coated composites. Sol Energ Mat Sol C 2010, 94: 1157–1165. 10.1016/j.solmat.2010.03.003View ArticleGoogle Scholar
- Wang J, Xie Y, Zhang Z, Li J, Chen X, Zhang L, Xu R, Zhang X: Photocatalytic degradation of organic dyes with Er3+:YAlO3/ZnO composite under solar light. Sol Energ Mat Sol C 2009, 93: 355–361. 10.1016/j.solmat.2008.11.017View ArticleGoogle Scholar
- Khataee A, Marandizadeh H, Vahid B, Zarei M, Joo SW: Combination of photocatalytic and photoelectro-Fenton/citrate processes for dye degradation using immobilized N-doped TiO2 nanoparticles and a cathode with carbon nanotubes: central composite design optimization. Chem Eng Proces 2013, 73: 103–110.View ArticleGoogle Scholar
- Rajamanickam D, Shanthi M: Photocatalytic degradation of an azo dye Sunset Yellow under UV-A light using TiO2/CAC composite catalysts. Spectrochim Acta A 2014, 128: 100–108.View ArticleGoogle Scholar
- Konstantinou IK, Albanis TA: TiO2-assisted photocatalytic degradation of azo dyes in aqueous solution: kinetic and mechanistic investigations: a review. Appl Catal B Environ 2004, 49: 1–14. 10.1016/j.apcatb.2003.11.010View ArticleGoogle Scholar
- Rahman QI, Ahmad M, Misra SK, Lohani M: Effective photocatalytic degradation of rhodamine B dye by Zno nanoparticles. Mater Lett 2013, 91: 170–174.View ArticleGoogle Scholar
- Wang X, Wu P, Lu Y, Huang Z, Zhu N, Lin C, Dang Z: NiZnAl layered double hydroxides as photocatalyst under solar radiation for photocatalytic degradation of orange G. Sep Purif Technol 2014, 132: 195–205.View ArticleGoogle Scholar
- Jamal A, Rahman MM, Khan SB, Faisal M, Akhtar K, Rub MA, Asiri AM, Al-Youbi AO: Cobalt doped antimony oxide nano-particles based chemical sensor and photo-catalyst for environmental pollutants. App Surf Sci 2012, 261: 52–58.View ArticleGoogle Scholar
- Khan SB, Chani MTS, Karimov KS, Asiri AM, Bashir M, Tariq R: Humidity and temperature sensing properties of copper oxide-Si-adhesive nanocomposite. Talanta 2014, 120: 443–449.View ArticleGoogle Scholar
- Rahman MM, Jamal A, Khan SB, Faisal M: Humidity and temperature sensing properties of copper oxide–Si-adhesive nanocomposite. Biosens Bioelectron 2011, 28: 127–134. 10.1016/j.bios.2011.07.024View ArticleGoogle Scholar
- Kim D, Jang M, Seo J, Nam K-H, Han H, Khan SB: UV-cured poly(urethane acrylate) composite films containing surface-modified tetrapod ZnO whiskers. Compos Sci Technol 2013, 75: 84–92.View ArticleGoogle Scholar
- Faisal M, Khan SB, Rahman MM, Jamal A: Role of ZnO-CeO2 nanostructures as a photo-catalyst and chemi-sensor. J Mater Sci Technol 2011, 27: 594–600. 10.1016/S1005-0302(11)60113-8View ArticleGoogle Scholar
- Yang H, Hu Y, Zhang X, Qiu G: Mechanochemical synthesis of cobalt oxide nanoparticles. Mater Lett 2004, 58: 387–389. 10.1016/S0167-577X(03)00507-XView ArticleGoogle Scholar
- Sun C-G, Tao L, Liang H-J, Huang C-J, Zhai H-S, Chao Z-S: Preparation and characterization of hexagonal mesoporous titanium-cobalt oxides. Mater Lett 2006, 60: 2115–2118. 10.1016/j.matlet.2005.12.084View ArticleGoogle Scholar
- Rahman MM, Jamal A, Khan SB, Faisal M: Characterization and applications of as-grownb-Fe2O3 nanoparticles prepared by hydrothermal method. Nanoparticle Res 2011, 13: 3789–3799. 10.1007/s11051-011-0301-7View ArticleGoogle Scholar
- Aronniemi M, Lahtinen J, Hautojarvi P: Characterization of iron oxide thin films. Surf Interface Anal 2004, 36: 1004–1006. 10.1002/sia.1823View ArticleGoogle Scholar
- Mohapatra L, Parida KM: Zn-Cr layered double hydroxide: visible light responsive photocatalyst for photocatalytic degradation of organic pollutants. Separat Purif Technol 2012, 91: 73–80.View ArticleGoogle Scholar
- Parida KM, Mohapatra L: Carbonate intercalated Zn/Fe layered double hydroxide: a novel photocatalyst for the enhanced photo degradation of azo dyes. Chem Eng J 2012, 179: 131–139.View ArticleGoogle Scholar
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