Azar
Sadollahkhani
*ab,
Iraj
Kazeminezhad
b,
Jun
Lu
c,
Omer
Nur
a,
Lars
Hultman
c and
Magnus
Willander
a
aDepartment of Science and Technology, Campus Norrköping, Linköping University, SE-60174 Norrköping, Sweden. E-mail: azar.sadollah.khani@liu.se; azarkhanny@gmail.com
bNanotechnology Lab, Department of Physics, Shahid Chamran University, Ahvaz, Iran
cThin Film Physics Division, Dept. of Physics, Chemistry and Biology (IFM), Linköping University, Linköping, Sweden
First published on 4th August 2014
ZnO nanoparticles were synthesized by co-precipitation with no capping agent followed by covering with ZnS using a solution-based chemical method at low temperature. By variation of the solution concentrations it was found that the fully-covering ZnS shell forms by a reaction of Na2S with ZnO NPs followed by the formation of ZnS nano-crystals by the reaction of Na2S with ZnCl2. The mechanism that led to full coverage of the ZnO core is proposed to be the addition of ZnCl2 at a later stage of the growth which guarantees a continuous supply of Zn ions to the core surface. Moreover, the ZnS nano-crystals that uniformly cover the ZnO NPs show no epitaxial relationship between the ZnO core and ZnS shell. The slow atomic mobility at the low reaction temperature is attributed to the non-epitaxial uniform ZnS shell growth. The rough surface of the ZnO grains provides initial nucleation positions for the growth of the ZnS shell nano-crystals. The low growth temperature also inhibits the abnormal growth of ZnS grains and results in the homogeneous coverage of ZnS nano-crystals on the ZnO core surface. The as-synthesized ZnO@ZnS core–shell nanoparticles were used as a photocatalyst to decompose Rose Bengal dye at three different pH values. ZnO@ZnS core–shell nanoparticles perform as a more active photocatalyst at a pH of 4, while pure ZnO nanoparticles are more efficient at a pH of 7.
Today's global problem of water pollution is cause to a large extent by dyeing, which is mainly due to printing industries that discharge their effluent into the natural water resources without any treatment.27–29 Different methods and materials have been developed alleviate this problem. TiO2 has been used as a photocatalyst to degrade different dyes and pollutants, but further investigation has shown that ZnO not only has similar efficiency of photocatalytic degradation but also it is a better substitute for TiO2 in some applications.30–32 Since covering ZnO with different semiconductors changes the electronic states and the surface of the ZnO NPs, this could affect its photocatalytic activity.33 The other issue that needs to be considered is related to the photocatalytic activity of NPs at different pH values. As dyes pollutants can be found in different mediums, investigating the photocatalytic efficiency of products at different pH values can provide useful information.
In this work, we show a simple fast reliable method to grow ZnO@ZnS CSNPs with full coverage using a simple two steps low temperature chemical method. In this way the ZnO NPs are covered with ZnS without using any additional capping agent between them. The products were prepared with different concentration of the sulfur source and were characterized by X-ray diffraction (XRD), Fourier transform infrared spectroscopy (FTIR), scanning electron microscopy (SEM), high-resolution transmission electron microscopy (HRTEM), and energy dispersive X-ray spectroscopy (EDX) mapping. Finally, the as-synthesized ZnO@ZnS CSNPs were successfully used as a photocatalyst to degrade Rose Bengal at different pH values.
The structural characterization of ZnO@ZnS CSNPs was investigated by X-ray powder diffraction (XRD) using a Phillips PW 1729 powder diffractometer equipped with CuKα radiation (λ = 1.5418 Å) operating at a generator voltage of 40 kV and a current of 40 mA. A LEO 1550 Gemini field emission scanning electron microscope working at 15 kV was used to investigate the morphology of the ZnO@ZnS CSNPs. An Equinox 55 FT-IR spectrometer was used in order to reach further information about the products and their surfaces. The HRTEM characterization was carried out by using a FEI Tecnai G2 TF20 UT instrument with a field-emission gun operated at 200 kV. The instrument has a point resolution of 0.19 nm and is equipped with an EDX system. The TEM specimen was prepared by dispersing the nanostructure powder on a copper grid with a thin amorphous carbon film. A Perkin Elmer Lambda 900 UV-visible spectrophotometer was used to investigate the photocatalytic activities of the as-synthesized ZnO@ZnS CSNPs.
A home-made photo reactor equipped with four 18 W UV lamps (256 nm) was used to perform photocatalytic experiments. 0.05 g of each sample material was used as photocatalyst after mixing with 100 mL of the aqueous Rose Bengal dye solution with an initial concentration of 40 mg L−1. The dye solutions were prepared with different pH values using three various buffers (4, 7, and 10) in order to investigate the rate of dye removal at different pH values. The solution was put on stirring for 30 min until adsorption equilibrium was achieved then the solution was kept in the reactor and exposed to the UV light. In order to determine the dye concentration using UV-Vis spectrophotometer, some irradiated solution was withdrawn from the beaker each 20 min and their suspended samples were collected by centrifugation.
The crystalline size of the ZnO NPs was determined using the Scherrer formula:
ATR-FTIR spectroscopy was used to identify the capping of the ZnO NPs by the ZnS. Fig. 2 shows the FTIR spectra of the different samples. The peak which is observed from 400 cm−1 to 500 cm−1 is due to Zn–O vibrations of ZnO NPs. The peak at around 1100 cm−1 is the characteristic ZnS vibration peak that cannot be observed in the pure ZnO and this confirms that the ZnO nanoparticles capped with ZnS. This peak is absent from the pure ZnO NPs spectrum. Also as it can be seen in Fig. 2, the peak around 1100 cm−1 is increased by increasing the concentration of the sulfur source, and that indicates the presence of ZnS covering the ZnO NPs. The peak from 1500 cm−1 to 1650 cm−1 belongs to vibrations of H–O–H bond and the broad peak from 3200 cm−1 to 3650 cm−1 is due to the O–H variation of water molecules.
SEM imaging was carried out to determine the morphology of the pure ZnO NPs and to identify possible changes by covering. Fig. 3 shows the SEM images of ZnO NPs and the different ZnO@ZnS CSNPs. It can clearly be seen that, particles are not entirely spherical in shape and the agglomeration of ZnS-capped ZnO NPs is increased with increasing the concentration of the sulfur source. One can imagine that, each ZnO@ZnS CSNP includes a cluster of ZnO NPs which is covered with capping agent (ZnS) and it causes the increase in the size of the ZnO@ZnS CSNP compared to the pure ZnO NPs.
HRTEM is the most reliable technique to investigate whether or not the ZnO particles are covered with ZnS and for this reason a closed study was performed on the ZnO@ZnS CSNPs prepared with 0.05 M concentration of Na2S. The TEM image in Fig. 4a shows the grain of ZnO@ZnS CSNPs. The dimension of the ZnO core is approximately 200 nm long and 100 nm wide. The BF-TEM image also shows that the surface of the ZnO core is rather rough. For comparison, pure initial ZnO NPs were characterized as illustrated in Fig. 5a and the STEM of ZnO@ZnS CSNPs is also shown in Fig. 5b. The rough surface of ZnO is beneficial for the reaction of ZnO with Na2S and nucleation of ZnS. To characterize the crystallinity of ZnO NPs, the TEM sample was tilted and a selected area electron diffraction (SAED) pattern along the [110] zone axis of ZnO was obtained (see Fig. 4b). Furthermore, the ZnS shell structure was investigated by energy dispersive X-ray spectroscopy (EDX) mapping. Atomic concentration of Zn is the same for both ZnO and ZnS phases. Thus, to distinguish the ZnO from the ZnS, the distribution of sulfur and oxygen is critical. Fig. 4c exhibits that sulfur distributes on surface (shell), whereas oxygen is in the core region. Furthermore, the HRTEM image from the left corner of the ZnO@ZnS CSNPs is acquired and shown in Fig. 4d. Both the HRTEM image and the corresponding fast Fourier transform (FFT) pattern (Fig. 4e) show that the ZnS is polycrystalline. ZnO has hexagonal wurtzite structure and ZnS has cubic zinc blende structure and ZnS has a larger cell parameters. The circles in Fig. 4b and e indicate the reflections from polycrystalline ZnS phase. No epitaxial relationship between the ZnS and the ZnO was found. Epitaxial relationship between ZnO and ZnS was frequently found in some high temperature synthesized ZnO@ZnS samples18–21 in spite of a large mismatch between ZnO and ZnS structures. In this work, ZnS NPs are uniformly and randomly distributed on ZnO core surface because of the low atomic mobility at low temperature. Fig. 6 shows EDX mapping of the ZnO@ZnS CSNPs prepared with 0.05 M concentration of Na2S. It is clear that increasing the concentration of the S2− ions leads to formation of the more uniform and dense shell. Also, no ZnS NPs was observed in this concentration.
In order to investigate the ZnO@ZnS CSNPs formation mechanism, synthesis of the ZnO@ZnS CSNPs prepared with 0.05 M concentration of Na2S was repeated without addition of the ZnCl2. The result was compared with the case when ZnCl2 was added. Fig. 7a shows the XRD spectra of the ZnO@ZnS CSNPs with (denoted by A) and without (denoted by B) the addition of ZnCl2, respectively. It can be seen in Fig. 7a that the intensity of some peaks belonging to the ZnO are higher for the case without addition of the ZnCl2, which can be due to the covering of the ZnO NPs with a thicker shell. Also, a magnified XRD spectrum from 25° to 30° is shown as insert and indicating that the peak intensity belonging to the ZnS is higher for the sample prepared by the addition of the ZnCl2. Further information was obtained by studying the FTIR spectra for both cases. Fig. 7b shows the FTIR spectra of the ZnO@ZnS CSNPs with (denoted by A) and without (denoted by B) the addition of ZnCl2, respectively. It is clear that the characteristic ZnS vibration peak is higher in the ZnO@ZnS CSNPs prepared by the addition of the ZnCl2. This means that the number of Zn–S bands in the ZnO@ZnS CSNPs grown by adding the ZnCl2 has increased. Based on this we propose that the growth mechanism of fully covered ZnO@ZnS CSNPs in our procedure is as follows:
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Fig. 7 (a) XRD spectra of ZnO@ZnS CSNPs prepared (a) without and (b) with adding ZnCl2. (b) ATR-FTIR spectra, and (c) A schematic illustration of the ZnO@ZnS CSNPs formation mechanism. |
After dispersing the ZnO NPs in isopropanol, the pH of the solution was adjusted to around 10. As the ZnO NPs are soluble in acidic and basic media, the surface of the NPs will start dissolve and the S2− released from the Na2S which is added drop wise, will react with the Zn2+ and leads to produce ZnS around the ZnO NPs:
Zn2+ + S2− → ZnS |
The formation of a layer of ZnS separates the ZnO NPs from the sulfur ions in the solution so that no more reaction could proceed between the two. By adding the ZnCl2 to the mixture drop wise, the unreacted S2− ions around the shell will react with the Zn2+ from the solution forming more ZnS on the surface of the NPs. The formation mechanism of ZnO@ZnS CSNPs is shown in the schematic diagram of Fig. 7c.
In the work reported by Sharma et al.,25 before adding the nutrients to form the ZnO NPs the two ZnCl2 and Na2S solutions were mixed together, which leads to formation of ZnS nanoparticles in the solution before adding the ZnO NPs. Moreover, they did not explain how the ZnO NPs are covered with ZnS. To prevent the formation of any impurity in our work, Na2S solution was added to ZnO NPs drop wise and it was kept under continuous stirring for 2 h. After some of the S2− ions have reacted with the surface of ZnO NPs in the solution, the ZnCl2 solution is added to react with the unreacted S2− around the shell and form a dense shell with full coverage. Moreover, in our work all mixed solutions were added drop wise, and all mixtures were under stirring all the time so that the ions could be dispersed uniformly in the mixture and form identical particles. Hence, our sequence of the nutrients introduction to the synthesis of the ZnO@ZnS CSNPs has been rational and has resulted in full coverage.
h+ + H2O → OH˙ + H+ | (1) |
h+ + OH− → OH˙, | (2) |
e− + O2 → O2˙− + H+ → HO2˙ + O2˙− → HO2˙ + O− | (3) |
HO2˙ → H2O2 + O2 | (4) |
H2O2 + O2˙− → HO˙ + OH− + O2 | (5) |
H2O2 + e− → HO˙ + OH− | (6) |
H2O2 + hν → 2HO˙. | (7) |
Finally, the dye pollutant is decomposed by the generated agents:34
Dye + (O2˙− or HO˙ or OHO2˙) → intermediate → product | (8) |
Since the point of zero charge of a photocatalyst varies with pH, the adsorption of dye on the surface of the photocatalyst is different at various pH values. It is important to mention that the decomposition of some dyes occurs on the surface of the photocatalyst, so the adsorption of the dye is a crucial step in a photocatalytic degradation process. Although the dye with high adsorption degrades faster, the effect sites for absorbing the UV light decreases with increasing the adsorption of the dye on the surface of the photocatalyst. Moreover, higher pH value could provide higher concentration of hydroxyl ions to react with holes and form hydroxyl radicals which subsequently cause an increased photocatalytic degradation rate. The combined effect of the adsorption onto the photocatalyst and concentration of the hydroxyl radicals will determine the extent of the degradation.35
The chemical structure of the Rose Bengal dye is shown in Fig. 8. The Rose Bengal becomes negatively charged by losing the Na+ after dissolving in water and it can thus be adsorbed on positively charged surfaces. Initially, the dye adsorption on the surface of the ZnO NPs and the ZnO@ZnS CSNPs (ZnO@ZnS1 (0.025 M) ZnO@ZnS2 (0.05 M) and ZnO@ZnS3 (0.1 M)) was investigated at three different pH values (4, 7, and 10) and the results are summarized in Fig. 9 and according to this column chart, the maximum and minimum adsorption of the Rose Bengal takes place at pH of 4 and 10, for the ZnO@ZnS CSNPs and ZnO NPs, respectively and there was no adsorption on the surface of the ZnO NPs at pH of 10. Another important point which can be found from Fig. 8 is that the dye is adsorbed more on the surface of the ZnO@ZnS1 CSNPs and ZnO@ZnS2 CSNPs at each of the three pH values. This is because of the more defects and dangling bonds on the surface, which can act as traps for these two samples. To confirm this claim the photoluminescence spectra of each samples was prepared and is shown in Fig. 10. Table 1 shows the ratio of the near band edge (NBE) to the deep level emission (DLE) intensity of the all samples and indicate that the defects are decreasing gradually by filling up the oxygen vacancies via S atoms for the case of ZnO@ZnS1, and then it is increased even further for the ZnO@ZnS2 and for ZnO@ZnS3 is decreased again. Coating the surface of the particles with ZnS shell leads to filling up of the oxygen vacancies on the surface of the ZnO NPs with the S atoms. But for the ZnO@ZnS1 the concentration of the sulfur source is not enough to form a full shell, therefore the S atoms fill up some oxygen vacancies and decrease the DLE intensity. Although a lot of oxygen vacancies have been filled in ZnO@ZnS2 sample, its ZnS layer has more sulfur vacancies. With further increasing of the sulfur ions, a more uniform ZnS layer sediments on the ZnO NPs and forms a shell with fewer defects.
Sample | NBE to DLE ratio |
---|---|
ZnO | 0.18 |
ZnO@ZnS1 | 0.25 |
ZnO@ZnS2 | 0.08 |
ZnO@ZnS3 | 0.6 |
Fig. 11–13 show the photocatalytic removal of the Rose Bengal using ZnO NPs and ZnO@ZnS CSNPs after 120 min. and at three different pH values: 4, 7, and 10, respectively. More detailed results are shown in the plot of C/C0versus time, which is given in Fig. 14, where C0 is the initial concentration of the dye, C is the concentration of the dye after irradiation time t in min. It can be seen from Fig. 12a that, at a pH value of 4, almost 35%, 33%, 51%, and 37% of dye was degraded after 120 min illumination for ZnO NPs, ZnO@ZnS1, ZnO@ZnS2, and ZnO@ZnS3, respectively. According to these results, the photocatalytic activity of ZnO@ZnS2 and ZnO@ZnS3 is better than the ZnO NPs and the ZnO@ZnS2 with the most adsorption of dye performed better as a photocatalyst at pH 4. The plot of C/C0versus time for a pH of 7, namely Fig. 14b, indicates that the dyes was decomposed by 49%, 21%, 30%, and 28% for the ZnO NPs, ZnO@ZnS1, ZnO@ZnS2, and ZnO@ZnS3, respectively, and indicate that the ZnO NPs show better photocatalytic activity at this pH compared to the CSNPs. According to Fig. 14c, the Rose Bengal dye was degraded by about 50%, 35%, 50%, and 38% for ZnO NPs, ZnO@ZnS1, ZnO@ZnS2, and ZnO@ZnS3, respectively and shows almost the same photocatalytic activity for ZnO NPs and ZnO@ZnS1. Using graphene/polyaniline composite, Rose Bengal degradation was reported.36 In this work they employed a xenon arc lamp 300 W for 3 h. and they reported 50% dye removal. In our case we have used a 62 W UV lamp and achieved a 50% Rose Bengal degradation in 2 h. This shows that the presented use of ZnO@ZnS CSNPs as Rose Bengal degradation is efficient. The kinetics of the photocatalytic degradation of organic dyes usually follows the Langmuir–Hinshelwood mechanism:37
r = −dC/dt = (kKC)/(1 + KC), | (9) |
ln(C0/C) = kKt = Kappt, | (10) |
To explain the possible causes of the observed results, we note that, covering the ZnO NPs with ZnS leads to form a type II system. In type II systems, the effective band gap of the core–shell system is smaller than both the core and the shell material as it is clear in Fig. 16. Smaller band gap needs lower energy to produce electron–hole pairs and also leads to a more effective transfer of electrons between the core and the shell in addition to a relatively long lifetime of the photogenerated electron–hole pairs.38 These conditions lead us to the finding that the ZnO@ZnS CSNPs can show better photocatalytic efficiency, but in some cases electron–hole recombination occurs at the interface between the core and the shell material and this can reduce the photocatalytic activity of core–shell nanostructures.
The effect of the pH on the efficiency of the dye decolorization is difficult to assess because of the multiple roles of the pH of the solution. First, there is a possibility of the deionization state of the surface which influence the adsorption of dye onto the nanocatalyst. Second, the hydroxyl radicals, which are essential for photocatalytic process, can be formed by reaction between the positive holes and the hydroxyl ions. Positive holes are major species at low pH and hydroxyl ions are major at natural and high pH values. Thirdly, at low pH values the ZnO nanoparticles tend to agglomerate so that its surface will be decrease and this result in reduction of photocatalytic activity.39
All the above mentioned factors play a role in determining the photocatalytic efficiency and by considering all of them the photocatalytic behavior of one nanocatalyst at a specific pH is justified. According to the obtained results in this paper the ZnO@ZnS CSNPs show better photocatalytic efficiency at a pH of 4 compared to ZnO NPs. The possible reason behind this could be explained by the fact that the ZnO NPs agglomerate at this pH and this results in a reduction of effective surface for absorbing the UV light and also the adsorption of the dye while in ZnO@ZnS CSNPs, the holes which are the dominant species at low pH are even more due to the transferred holes from the core to the shell leading to an increase of the hydroxyl radicals. Also, as it was mentioned before the adsorption of the dye onto the surface of the ZnO@ZnS CSNPs is maximum at a pH of 4. This can also improve the photocatalytic activity. At a pH of 7 ZnO NPs show better photocatalytic behavior compared to the ZnO@ZnS CSNPs. ZnO NPs are not agglomerated at pH 7 and it seems that this increases the effective sights for absorbing UV light, which leads to improvement of its photocatalytic behavior compared to a pH of 4. For the ZnO@ZnS CSNPs, the photocatalytic activity has declined compared to pH 4, which is due to decreasing the adsorption of the dye onto the surface of the ZnO@ZnS CSNPs. At a pH 10 the photocatalytic behavior of the two photocatalysts is almost the same. It seems that at a pH of 10 the effective factor is increasing the amount of hydroxyl radicals. Increasing the amount of hydroxyl ions by increasing the pH, the higher concentration of the hydroxyl ions leads to higher concentration of hydroxyl radicals, which causes an enhanced photocatalytic decolorization rate.
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