† Corresponding author. E-mail:
Project supported by the International Cooperation Program of the Ministry of Science and Technology of China (Grant No. 2015DFR00720), the Cooperation Program of Wuhan Science and Technology Bureau, China (Grant No. 2016030409020219), and the Shenzhen Committee on Science and Technology Innovation, China (Grant No. JCYJ20170818112901473).
Undoped and praseodymium-doped zinc oxide (Pr-doped ZnO) (with 2.0-mol%–6.0-mol% Pr) nanoparticles as sunlight-driven photocatalysts are synthesized by means of co-precipitation with nitrates followed by thermal annealing. The structure, morphology, and chemical bonding of the photocatalysts are studied by x-ray diffraction (XRD), scanning electron microscopy (SEM) with energy dispersive x-ray emission spectroscopy (EDS), x-ray photoelectron spectroscopy (XPS), and Fourier transform infrared spectroscopy (FTIR), respectively. The optical properties are studied by photoluminescence (PL) and UV-vis diffuse reflectance spectroscopy (UV-vis DRS). We find that Pr doping does not change the crystallinity of ZnO; but it reduces the bandgap slightly, and restrains the recombination of the photogenerated electron–hole pairs. The photocatalytic performance of the photocatalysts is investigated by the photodegradation reaction of 10-mg/L rhodamine B (RhB) solution under simulated sunlight irradiation, showing a degradation rate of 93.75% in ZnO doped with 6.0-mol% Pr.
Pesticides, dyes, and heavy metals in water may cause environmental pollution.[1] Among these pollution sources, organic dyes are widely used in the leather, textile, pulp, cosmetic, and pharmaceutical industries and they are dominating pollutants in waste water. These dyes are toxic and carcinogenic, so they may affect the health of living things on Earth.[2–4] However, these stubborn organic pollutants are carbon-based chemical substances which are not easy to degrade naturally and may not be entirely eliminated by the conventional techniques or manner like biological, physical, and chemical processes. It can be of high operational cost to adopt the expensive chemicals and electricity consumption in order to remove the pollutants completely, owing to their stability to the oxidants, which consumes huge energy resources and produces perilous secondary pollutants, such as toxic sludge, heavy metals, and solid waste.[4–6]
Facing the problems of environmental pollution and exhaustion of energy sources, the search for new energy has attracted extensive attention of researchers. It has been proved that multi-phase semiconductors have great potential for the following applications in the new energy sector: photocatalytic and electrocatalytic production of hydrogen from water[7–10] and photocatalytic elimination of toxic chemicals in water.[11] Among the numerous semiconductors used in the field of photocatalysis such as ZnO,[12] ZnS,[13] TiO2,[14] and Fe2O4,[15] ZnO is one of the most common materials due to its stable chemical nature, low cost, and non-toxic characters.[16] It is widely used in solar cells, sensors, catalysts, luminescence, optoelectronics, biomedical devices, and light-emitting diodes.[17–20] However, its wide bandgap (3.37 eV) means that it can absorb only UV light (λ < 368.0 nm) that occupies only 3%–5% of the sunlight; this restricts the utilization of the complete solar energy spectrum and leads to low quantum efficiency.[21,22] Besides, the separation of photogenerated electrons from vacancies needs to be strengthened for enhancing the photo-quantum efficiency.[6] Therefore, making the ZnO photocatalyst respond to the solar spectrum and promoting the separation of photogenerated electron–hole pairs have become one of the biggest challenges.[23]
Researches in recent years have indicated that the performance of semiconductor photocatalysts can be enhanced through modification with metal and/or nonmetal doping, and the spectral response is also improved, with the better utilization of the sunlight.[24] Therefore, modified photocatalysis based on semiconductor oxides proves to be a good technology for treating the environmental pollution, and has become a rather popular research topic over the past few years.[25]
Rare earth doped materials applied to optical light-emitting phosphors and other optoelectronics devices have aroused broad interest.[26] Furthermore, rare earth materials are important for photocatalytic techniques because of the different special interband 4f–5d and intraband 4f–4f electronic transitions compared with other element groups. Hence, combining rare earth elements with a ZnO matrix may enable pollutants to be absorbed onto the photocatalyst surface.[27] There are 17 elements in lanthanide elements, but researches on rare earth-doped ZnO photocatalysts are still rather deficient. Matarangolo et al. reported that a Pr-doped ZnO photocatalyst showed the better photocatalytic performance for discolorating and mineralizing Eriochrome Black T in aqueous solution both under UV and visible-light illumination than Ce- or Eu-doped ZnO photocatalysts.[5] However, the photodegradation of the RhB dye in water by the Pr-doped ZnO photocatalyst under the solar light illumination has not been reported. For this reason, we intend to study the effects of Pr-dopant on the structural, morphologic, and optical properties of ZnO nanoparticles and to investigate the photocatalytic activity depending on Pr-dopant concentration tested in removal of RhB dye in aqueous solution under simulated sunlight irradiation.
In the present paper, Pr-doped ZnO samples are synthesized through co-precipitating by using zinc nitrate hexahydrate (Zn(NO3)2⋅6H2O), praseodymium nitrate hexahydrate (PrN3O9⋅H2O), trisodium citrate dihydrate (C6H5Na3O7⋅2H2O), and sodium hydroxide (NaOH), the microstructure, morphology, and optical features of photocatalysts are characterized by x-ray diffraction (XRD), scanning electron microscopy (SEM) equipped with energy dispersive x-ray spectrometer (EDS), x-ray photoelectron spectroscopy (XPS), Fourier transform infrared spectroscopy (FTIR), photoluminescence (PL), and UV-vis diffuse reflectance spectra (UV-vis DRS). The Rhodamine B (RhB) removal efficiency under simulated sunlight illumination is investigated to evaluate the photocatalytic activity of the prepared ZnO:Pr nanoparticles.
Zinc nitrate hexahydrate (Zn(NO3)2⋅6H2O), praseodymium nitrate hexahydrate (PrN3O9⋅H2O), trisodium citrate dihydrate (C6H5Na3O7⋅2H2O), and sodium hydroxide (NaOH) were used for the chemical synthesis. All these reactants were analytic reagents and no further purification was performed in the work. Deionized water was employed in all the synthesis processes.
A series of Zn1−xPrxO (with x = 0, 0.02, 0.04, 0.06) photocatalysts was synthesized by co-precipitating with nitrates. In a typical run, zinc nitrate hexahydrate and praseodymium nitrate hexahydrate were dissolved in 300-ml deionized water in a given value of substance ratio and agitated magnetically to obtain well-proportioned and stable solutions. After 15 min and 60 min, respectively, trisodium citrate dihydrate and sodium hydroxide were added to the solution. After 2 h, the magnetic mixer was turned off and the white precipitate was produced. Then, the precipitates were filtered separately and washed repeatedly with absolute ethyl alcohol to wipe off the unreacted chemicals. The product was then dried at 80 °C for 14 h. In this way, nanoparticle samples of ZnO, Zn0.98Pr0.02O, Zn0.96Pr0.04O, and Zn0.94Pr0.06O were produced. Finally, these samples were heated at a temperature of 240 °C for 2 h.
The structural characterization of the synthetic photocatalysts was carried out with an x-ray diffractometer (D8 Advance, BRUKER) by using Cu Kα radiation (λ = 0.1542 nm). The 2θ range is 20°–80° and the scanning step is 0.02°. The morphologies of the samples were observed by SEM (SIRION, FEI) along with EDS. The chemical compositions of the samples as well as the valences of elements were investigated by XPS (Thermo Fisher ESCALAB 250 Xi) and all spectra were calibrated with the C 1s core level spectrum at a binding energy of 284.6 eV. The infrared spectra were recorded by Fourier transform infrared (FTIR) spectroscopy (FTIR5700, Thermo USA) in a wavenumber range of 500 cm−1–4000 cm−1 to investigate the chemical bonds of the photocatalysts. The PL spectra were surveyed on a Raman spectrophotometer (RM1000, Renishaw) by using an Ar ion laser with an excitation wavelength of 325 nm. The UV-vis DRS spectra in a wavelength of 300 nm–600 nm were recorded through a UV-vis spectrophotometer (Lambda 35, PerkinElmer) with an integrating sphere for determining the bandgap of photocatalysts.
The photocatalytic properties of the samples were investigated by the photodegradation for RhB dyes. In a typical run, 5 mg of photocatalysts were suspended in 10 ml of RhB solution with a concentration of 10 mg/L. Then, the suspension was gently stirred for 30 min in the dark to make the photocatalyst well dispersed and to reach adsorption–desorption balance. Next, the suspensions were irradiated by a mercury-tungsten combined light lamp (300 W, involving the UV and visible light region to simulate the solar conditions). A 2-ml suspension was sampled at 15-min intervals for centrifuging at a speed of 5000 rpm for 5 min. Then, the supernatant liquid of the solution was poured into a quartz glass, and the UV-vis absorption spectra ranging from 650 nm to 450 nm in wavelength were recorded by an S2500 spectrophotometer (UV-2550, SHMADZU) to monitor the process of photodegradation. The concentration of RhB was determined by the absorbance value of the solution located at 554 nm of the UV-vis spectrum.
Figure
It is worth noting that in a range of 30°–33° of the XRD spectrum (Fig.
The average crystallite sizes of the as-obtained nanoparticles were estimated by the peaks at a diffraction angle of 36° by using Debye–Scherrer’s equation:
Figures
The elemental composition and chemical bonds in Pr-doped ZnO samples are measured and the incorporation of Pr into ZnO lattice was confirmed by the XPS analysis. The XPS scan in a binding energy range of 0 eV–1300 eV of the 2.0-mol% Pr-doped ZnO shows that the photocatalyst consists mainly of Zn, O, and Pr element[27] (Fig.
To identify the presence of functional groups, FTIR spectra of pure and Pr-doped ZnO photocatalysts are measured, and the results are shown in Fig.
To investigate the optical properties, room temperature photoluminescence is measured in the wavelength range of 350 nn–800 nm as shown in Fig.
To investigate the optical absorption properties, the UV-vis DRS spectra in a range 300 nm–600 nm are measured as shown in Fig.
To study the photocatalytic properties of the synthesized samples with different Pr dopant concentrations, the photocatalytic degradation process of rhodamine B in aqueous solution under a simulated sunlight illumination is measured as shown in Figs.
ZnO compounds with different doping concentration Pr (0 mol%–6.0 mol%) photocatalysts are prepared by the facile co-precipitating method. XRD and SEM analyses show that the photocatalysts are of hexagonal wurtzite phase and spherical morphology. XPS analysis shows the Zn–O and Pr–O bonding existing in the Pr-doped ZnO samples, which is supported by the FTIR measurement and reveals the chemical bonding and the presence of doping-related functional groups. The PL spectrum suggests the restraint of recombination rate of the photogenerated electrons and holes. UV-vis DRS shows that the bandgap for Pr-doped ZnO decreases slightly after Pr doping. The photocatalytic results show a 93.75%-degradation of rhodamine B by 6.0-mol% Pr-doped ZnO photocatalyst under the irradiation of simulated sunlight for 45 min.
[1] | |
[2] | |
[3] | |
[4] | |
[5] | |
[6] | |
[7] | |
[8] | |
[9] | |
[10] | |
[11] | |
[12] | |
[13] | |
[14] | |
[15] | |
[16] | |
[17] | |
[18] | |
[19] | |
[20] | |
[21] | |
[22] | |
[23] | |
[24] | |
[25] | |
[26] | |
[27] | |
[28] | |
[29] | |
[30] | |
[31] | |
[32] |