Md Abdul Mumin,
Golam Moula and
Paul A. Charpentier*
Department of Chemical and Biochemical Engineering, University of Western Ontario, London Ontario, Canada N6A 5B9. E-mail: pcharpentier@eng.uwo.ca; Fax: +1 519 661 3498; Tel: +1 519 661 3466
First published on 3rd August 2015
Semiconductor quantum dots (QDs) sensitized onto nano TiO2 as heterogeneous photocatalysts have drawn considerable interest over the past few years. However, stability of the QDs attached to TiO2 and consistent photocatalysis are still major challenges of this approach. We describe herein, a facile process to fabricate nanocomposites from porous TiO2 nanowires and bare CdS and core–shell CdS–ZnS QDs, where the QD particles are linked covalently to the titania surface through a bifunctional organic linker, mercapto propionic acid (MPA). A thin layer of ZnS was grown on 6 nm CdS QDs to restrain the photocorrosion and passivate the trap states, enhancing the photoluminescence and quantum yield. The bifunctional linking molecule, MPA, was found to effectively disperse and stabilize the QD nanoparticles. The photocatalytic activities of the prepared catalysts were evaluated under ultraviolet and visible light solar irradiation for the photodegradation of methylene blue (MB), an organic dye. The decomposition rate of MB was enhanced as follows: CdSZnS–MPA–TiO2 > CdS–MPA–TiO2 > CdSZnS–TiO2 > CdS–TiO2 > TiO2 > P25. A maximum photodegradation efficiency of MB dye (∼88%) was obtained by core–shell CdS–ZnS QDs linked with nano TiO2. After 3 cycling tests of degradation, the loss of photoactivity was significantly minimized (from 68% to 10%) by CdSZnS–MPA–TiO2 compared to CdSZnS–TiO2 (by direct deposition).
To break the bottleneck, there have been various attempts to enhance and expand the optical absorption range of TiO2 and improve the separation efficiency of photogenerated electron–hole pairs. Recently, semiconductor quantum dots (QDs) have been attracting extensive attention to sensitize TiO2 due to their unique size dependent optoelectronic properties and the possibility of multiexciton generation. A lower band gap QD like CdSe, CdS with higher conduction band (CB) can enhance the electronic conversion efficiency of TiO2.7–9 The photogenerated electrons from the CB of the light activated QD can be injected into the non-activated TiO2, while the holes remain on the QD particles, leading to efficient and longer charge separation, increased UV absorption, as well as extending the absorption to the visible range.10,11 But, uniform deposition and stability of QD particles on TiO2 is often a problem due to the lack of attachment approaches and poor surface interactions under typical experimental conditions.12 A favourable link between QDs and TiO2 nanoparticles can minimizes these drawbacks, also enhancing the transfer of electron injection.7,13
Recently, intensive efforts have been undertaken to link bare QDs with nano TiO2 for photocatalysis applications.14–16 Mostly, long aging time (more than 24 hours) and high temperatures (200–400 °C) are required for improving the coupling of the two semiconductor materials and their crystallinity.17 In previous works, most attention has been paid to the synthesis and optical properties rather than activity and stability during photodegradation. Possible interactions between porous 1D TiO2 nanostructures and the effect of the bifunctional linking molecules to core–shell QDs needs to be investigated. Although, it has been reported by many researchers that compared to bare QDs, core–shell structured QDs with a thin shell of a higher band gap element are advantageous and have been shown to enhance photo-physical properties.18–20 This is attributed to the surface defects in the core acting as temporary ‘traps’ for the electron, hole or excitons, quenching radiative recombination and reducing the quantum yield (QY).21 Notably, CdS is an important photosensitizer of TiO2 and its size dependent optical properties have also been observed and reported by many researchers.6,22 Recently, we have shown that, by forming a thin shell of ZnS on CdS cores, the QY can be improved up to 50%, which is usually less than 20% for bare CdS QDs.23 The thin shell also minimizes the surface crystal defects and aggregation tendency of CdS, resulting in better particle separation which is very important for the photosensitization of TiO2 catalyst. Therefore, it is anticipated that by developing a novel facile coupling approach for more quantum efficient and stable core–shell QDs with nanoTiO2 using mild conditions, the activity and stability of the TiO2 photocatalyst can be improved.
Supercritical CO2 (scCO2) has emerged as a viable “green” alternative to hazardous organic solvents, as CO2 is cheap, non-toxic, non-flammable, and environmentally benign with low critical temperature and pressure (Tc = 31.1 °C, Pc = 7.38 MPa).24 The unique advantages of scCO2 include: (i) a “zero” surface tension, allowing penetration into pores that is not possible with organic solvents, (ii) low gas-like viscosities that enhance mass transfer and reaction kinetics, (iii) a liquid-like density and a gas-like diffusivity, and the solubility of solute is tuneable with both temperature and pressure.25 We recently reported that TiO2 nanowires synthesized using a sol–gel method in supercritical carbon dioxide (scCO2) are nano-structured with high specific surface area and porosity, and anatase in nature.25–28 During sol–gel chemistry, scCO2 has several roles, acting as a solvent, a modification agent, and a cleaning and a drying agent.29
Structurally, TiO2 exists in three polymorphs: anatase, rutile, and brookite. It is well accepted that anatase TiO2 exhibits higher photocatalytic activities than rutile and brookite TiO2.30,31 The indirect band gap anatase shows a longer charge carrier lifetime to participate in surface reactions compared to direct band gap rutile and brookite TiO2. Anatase TiO2 also enhances faster migration of photogenerated electrons and holes from the interior to the surface, resulting in a lower recombination rate for charge carriers.30,31 However, the anatase phase is thermodynamically metastable, so synthesis of anatase TiO2 with better quality including thermal stability is always an important parameter.13 Compared to TiO2 nanoparticles, TiO2 nanowires or nanotubes have been shown to be more effective in solar harvesting applications as their orientation provides excellent percolation pathways for vectorial charge transfer.7 Thakur et al. observed that the presence of CdS hinders the transformation of anatase to rutile even after annealing at 600 °C, attributed to the surface defect sites of anatase particles being occupied by CdS.10 However, they observed no specific morphology of both CdS and TiO2 nanoparticles and irregular distribution. Therefore, besides the one-dimensional orientation and well crystallized anatase, the strong interactions and uniform distribution of quantum efficient QDs (e.g. core–shell QDs) with TiO2 is still a major challenge that plays a key role to enhance both the activity and stability of the nanocomposite catalysts.
In the present work, highly photoluminescent and monodispersed CdS bare and CdS–ZnS core–shell quantum dots were prepared by using a facile and modified (changing reaction temperature and duration) colloidal synthesis approach. TiO2 nanowires were synthesized in scCO2 using sol–gel polycondensation of Ti-alkoxides and acetic acid. Then, by using a novel facile approach, calcined TiO2 nanowires were functionalized by a commercially available bifunctional linker (mercapto-propionic acid) and covalently attached to bare or core–shell QDs. The photocatalyst samples were characterized in detail and the energy transfer mechanism investigated. Finally, the experimental catalysts were investigated for degradation of methylene blue, an organic dye under UV, visible, and also simulated solar lights and the results compared with bare TiO2 and directly deposited QDs in TiO2.
Direct deposition of QDs on TiO2 was carried out following the previously reported method.7
Prior to irradiation, the Pyrex beaker containing the dispersion was stored in the dark for 30 min to reach adsorption/desorption equilibrium. At a given time interval, 4 mL aliquots were sampled and centrifuged (6000 rpm, 10 min) to separate the particles. The MB concentration in the aliquots was measured by UV-visible spectrophotometer monitoring the absorption maximum at 664 nm. A calibration plot was established relating the absorbance to the concentrations of MB. In each case, blank experiments were also conducted with the catalysts in the absence of light and MB without the catalysts under light irradiation. Moreover, reference experiments were also performed under the same conditions with commercial TiO2 (Degussa, P25) and synthesized TiO2 nanowires.
The photodegradation of MB for CdSZnS–MPA–TiO2 nanowires was also carried out under simulated sunlight (Model: LZCX1CH1, Luzchem, Canada, 300 W Xenon Lamp) without using any UV cut off filter for two intensities, 14 and 28 mW cm−2 and variable catalyst loading concentrations. The UV intensity was measured by using a UV A/B meter (Model: ST513, Sper Scientific Ltd). To examine the production of hydroxyl radical (OH˙) during photocatalytic reaction, a 3 × 10−4 M terephthalic acid solution in dilute NaOH solution (2 × 10−3 M) was mixed with the experimental photocatalysts under UV light illumination (intensity = 11.05 mW cm−2).34 Then the photoluminescence (PL) emission at 425 nm was observed at different intervals using the excitation wavelength of 315 nm.35
Splitting to three peaks at angles (2θ degree) 24–30 region represents the formation of hexagonal crystallinity rather than a single broad peak representing the cubic CdS QDs.36 In the case of CdS–ZnS core–shell QDs, the slight increase of the peaks at 28.2, 43.9, and 52.1 is due to the contribution of the planes (111), (220), and (311) of the zinc-blended ZnS nanocrystals (ICDD PDF 05-0566), which confirms the presence of ZnS with CdS.37 After core–shell formation, no peak broadening or intensity lowering was observed, which is attributed to the high degree of crystallinity from the presence of the thin ZnS shell, that can preserve the quantum properties of the hexagonal CdS core.38 Based on the Debye–Scherrer equation, the average particle size for CdS and CdS–ZnS QDs were calculated as 5.5 and 6.2 nm respectively. TiO2 nanowires (Fig. 1c) consists of the anatase phase with diffraction peaks at 25.2, 38, 48.2, 54.4, 63.1, 69.3, and 76.6 (JCPDC 21-1272).14 No peaks belonging to any other phase of TiO2 were detected, indicating the high purity of the synthesized products. After low loading (<5 weight%) of both types of QDs, the XRD patterns displayed rather weak QD peaks that were more prominent in the case of higher loading. Fig. 1d and e shows bare CdS and core–shell CdS–ZnS QDs (10%) covalently linked with TiO2 respectively. In both cases, there are additional peaks at 2θ of 28.2, 44, and 52.2, which are attributed to (101), (110), and (112) crystal planes of wurtzite CdS phase and (111), (220), and (311) of the zinc-blended ZnS. The other diffraction peaks of both CdS were not clearly resolved because they overlapped with that of anatase TiO2. There was no significant change of the anatase TiO2 peaks after QD loading, resulting from the high crystallinity of the nanocomposite products.
The morphology of both types of QDs were studied using TEM as shown in Fig. 2a and b. Both samples were present in a dispersed state, showing formation of individual nanoparticles, although better particle separation was observed after core–shell formation. Here, the thin shell of ZnS minimizes the surface crystal defects and aggregation tendency of CdS. The average particle size was found as 6 ± 1 nm for both bare and core–shell QDs respectively.
As shown in Fig. 2c, the TEM image reveals that TiO2 formed nanowires had an average diameter of 50 nm with a smooth surface. Here, the formation of individual nanowires by inhibiting their agglomeration is due to controlled nanowire growth in the absence of surface tension under supercritical CO2.39 In the case of direct deposition by in situ CdS–ZnS QDs synthesis in the presence of TiO2, QDs were observed agglomerated as seen in Fig. 2d. There was also a decrease in nanowire length observed because of vigorous stirring under high temperature during pyrolysis of the QD precursor. Whereas when using MPA linker, the aggregation of nanowires was efficiently overcome and the dispersion of QDs on the TiO2 surface was improved, which enhanced the interaction between QDs and TiO2 (Fig. 2e and f). This close contact and porous nature of the nanowires is very useful for the electron transfer from QDs to TiO2, which can potentially limit the recombination of photogeneration electrons and holes.40 With a closer look at these nanowires (Fig. 2g and h), the dispersed dark and black spots confirms the QDs are bound to the nanowire surface of the TiO2–QD assembly. The size of these dark spots matches with the size of the CdS and CdS–ZnS QDs. The chemical composition of these spots was further confirmed by SEM-EDX and XPS analysis (described below).
The morphology of the pure TiO2 and QDs/TiO2 nanocomposites was also observed by SEM as shown in Fig. 3. As is apparent from Fig. 3a, the TiO2 was formed as nanowires, which are 50 nm in diameter and 2–5 μm in length. The surface of the pure TiO2 nanowires is relatively smooth. Similar to the TEM results, SEM analysis also shows agglomeration of QDs and TiO2 in the case of direct deposition (Fig. 3b). This agglomeration was effectively reduced after linking of both CdS and CdS–ZnS QDs with TiO2 nanowires (Fig. 3c and d). In both cases, the surface became quite rough compared to pure TiO2. The surfaces were analyzed by SEM-EDX, and the results reveal that all the heteroarchitectures are mainly composed of titanium (Ti), oxygen (O), cadmium (Cd), sulfur (S), and zinc (Zn), confirming that the CdS and CdS–ZnS QD particles were successfully loaded onto the TiO2 nanowires.
During the synthesis of core–shell QDs, a TOA/TOP 2
:
1 ratio was used that was previously found best to form a thin layer on the QD surface, helping to minimize agglomeration for enhancing optical properties.41 TOA and TOP are organic and the resulting QDs are hydrophobic in nature.42 In the case of direct deposition, the QDs are less likely to adsorb to the hydrophilic surface of the TiO2 nanowires. During the photocatalytic reactions and also washing in the case of cyclic operation, there is a possibility of desorption of these directly deposited QDs from the TiO2 surface.
However, in the presence of mercaptopropionic acid (MPA), the mercapto end easily adsorbs onto the QD surfaces by replacing the initial surface passivation ligands (TOA/TOP). The carboxylic end of the linker binds with the hydrophilic surface of TiO2 nanowires.42,43 Because of the excellent distribution of the QDs on TiO2 and their better contact (as observed from TEM and SEM analysis), the covalently linked photocatalyst samples are anticipated to show enhanced photocatalytic efficiency than that obtained from direct deposition.
Fig. 4 shows the FTIR transmission spectra of free MPA (bifunctional linker), calcined TiO2 nanowires, and CdS–ZnS QDs linked with TiO2 nanowires. FTIR was employed to examine whether the –COOH group of MPA was chemically linked to the TiO2 nanowire surface and if the –SH group was chemically bonded to the QD surface. In the case of TiO2, the band at about 1617 cm−1 corresponding to the bending vibration of H–O, and the broad band starting from 900 cm−1 is assigned to the stretching of Ti–O–Ti.10 Free MPA provides strong bands at 1698 and 1424 cm−1, are typical for the asymmetric C
O and symmetric C–O stretching peaks of carboxylate (Fig. 4a). The 2500–2600 cm−1 band corresponds to the –SH group and a broad band in the range 2800–3200 cm−1 is attributed to the O–H band of MPA.14 The FTIR spectra of bare TiO2 was modified after linking CdS–ZnS QDs through the bifunctional linker MPA, as shown in Fig. 4b. There are at least three significant changes between free MPA and QDs–MPA–TiO2; (1) there is no C
O peak for QDs–MPA–TiO2 at 1698 cm−1, however, at the multiple carboxylate region (1510–1655 cm−1), a well-resolved band at 1584 cm−1 is evolved; (2) the broad O–H band of carboxylate at 2800–3200 cm−1 is absent for QDs–MPA–TiO2; (3) there is no –SH group peak at 2500–2600 cm−1. The first two changes provide clear evidence for the attachment of the –COOH group of MPA to the TiO2 surface, and the third change indicates the absence of the free mercapto groups and the formation of robust bonding between QD and MPA.14
![]() | ||
| Fig. 4 FTIR spectra of (a) 3-mercaptopropionic acid (MPA), (b) CdS–ZnS QDs–MPA–TiO2, and (c) TiO2 nanowires prepared under supercritical CO2 and calcined at 450 °C. | ||
XPS was carried out to further investigate QD nanoparticles linking to TiO2, the chemical composition of the nanocomposites and the valence state of various species present therein. The full survey scan over a large energy range at low resolution indicates the presence of Ti, O, and C in TiO2 (Fig. 5a), and Ti, O, C, Cd, Zn, and S in CdS–ZnS QDs linked with TiO2 (Fig. 5b). In the high resolution XPS spectra it is clearly seen that, the spin–orbit components (2p3/2 and 2p1/2) of the Ti 2p peak were deconvoluted into two curves at 454.7 and 460.4 eV, corresponding to Ti4+ in a tetragonal structure. The measured separation between these two peaks was 5.7 eV, which is consistent with the binding energy separation observed for stoichiometric TiO2.6 After both bare CdS and core–shell CdS–ZnS QDs linking with TiO2, both these peaks exhibited a slight shift due to chemical attachment of QDs with TiO2 through the linker and transferring the electrons from QDs into the TiO2 lattice.29 However, in both cases the separation of the peaks remained as 5.7 eV, confirming the high quality of TiO2 after QD loading. The C 1s spectrum exhibits two peaks located at 281.2 and 285.2 eV corresponding to C–H and C–O respectively. For bare TiO2, hydrocarbon is related to the residual carbon coming from the decomposition of the titanium precursor and some surface contaminants during XPS analysis.44 But the intensity of the same peak was increased after QD loading because of additional hydrocarbon from the linker molecule. The peak of C–O at 285.2 eV, and absence of any peak for C
O and O–C
O (at 288–290 eV) confirms the successful attachment of the linker with the TiO2 surface. Similarly, the O 1s shows a major peak at 526.3 eV attributed to crystal lattice oxygen (OTi–O). There was no peak for surface hydroxyl group (OO–H) at around 530 eV was observed. In the photoelectron spectrum of Cd 3d, the peaks at 401.5 and 408.2 eV are assigned for Cd 3d5/2 and 3d3/2 respectively. The spin–orbit separation of these peaks is 6.7 eV, which corresponds to the presence of the oxidation state +2 of Cd at the surface.6 The S 2p core level spectrum indicates the significant peak at 159 eV corresponding to S−2 of QDs. The presence of other peaks at 165.2 eV is due to the formation of S–S bond between the linker and the QDs.37 The Zn 2p core-level XPS spectrum of CdS–ZnS QDs before and after linked with TiO2 showed the doublet spectral lines at 1018 eV (Zn 2p3/2) and 1041 eV (Zn 2p1/2) with a spin–orbit separation of 23 eV, which corresponds to the Zn2+ oxidation state and is in good agreement with the previously published value of ZnS.45 The results of the XPS measurement, together with FTIR analysis and SEM-EDX measurement suggests that both QDs were successfully loaded and linked with TiO2 nanowires.
As shown in Fig. 6b, the absorption intensity in the region 400–510 nm was increased with the increase of CdS–ZnS QDs linking to TiO2. For the lower loading (<5%), there was only a small change in the intensity, however in the case of 10% loading a stronger absorbance was observed in that region. With a further increase of QD loading, there was no significant change in the intensity, which can be attributed to the aggregation of QDs that causes non-radioactive light emission, and also the crystal growth of QDs, leading to poor photo-sensitization.39 It was also observed that with more than 10% loading, TiO2 loses its hydrophilicity nature, which will reduce the dispersion ability of those nanocatalysts in the aqueous solution of organic dye/pollutants during the photocatalytic activity study.
Although aqueous synthesis of QDs is convenient, the quality and stability of the QDs are better when synthesized in organic solution.42 TOA/TOP capped QDs remain highly dispersible in organic solvents such as toluene and chloroform, and a stable photoluminescence was observed after two months for the samples kept under dark and at room temperature (data not shown). We have previously reported that, compared to a fluorescent dye, CdS QDs can minimizes photobleaching by 70% under continuous exposure of excited UV light.32 In addition, a thin layer of ZnS on the CdS QDs further enhances the photostability, as the ZnS shell suppresses the photochemical degradation of CdS, protecting the exciton wavefunction from nonradioactive recombination processes as surface traps.48 When the QDs are attached with a linker or ligand, the optical properties and stability are often improved.33 Therefore, it is anticipated that linking with MPA and loaded onto TiO2 nanowires enhances the photostability of both the core CdS and core–shell CdS–ZnS QDs.
Between bare CdS and core–shell CdS–ZnS QDs, core–shell QDs linked on TiO2 nanowires showed higher efficiency (88% compared to 64% in first 40 min). We previously reported that the thin ZnS shell helps to minimize any surface crystal defects and decrease the aggregation tendency of the bare CdS QDs, providing uniform dispersion and increasing the quantum yield from 25% to 48%.23 In contrast, under artificial solar irradiation (>365 nm), bare TiO2 exhibited a very small activity up to 15% photo-degradation of MB (Fig. 7b), mainly because of the absorption in the region 365–400 nm. CdS–ZnS QDs–MPA–TiO2 showed the highest MB decomposition under both visible and UV irradiation. After 180 min, 85% of MB was degraded with this photocatalyst, whereas 70 and 59% was decomposed by CdS–MPA–TiO2 and CdSZnS–TiO2 respectively. This result shows that both the UV and visible light induced catalytic efficiency of TiO2 nanowires was significantly enhanced by QDs linking, especially core–shell QDs than bare QDs.
In addition, the synthesized photocatalysts can be recycled and reused several times without a significant loss of efficiency, which is a key requirement for large scale application.49 In the case of direct deposited CdS–ZnS QDs onto TiO2 nanowires, after the first cycle there was more than 50% decomposition of MB observed, whereas this efficiency decreased significantly after the second and third cycles to 35 and 16% respectively. This reduction of efficiency is attributed to detachment of QDs from TiO2 surfaces during photocatalytic reaction and washing. In contrast, the covalently attached CdS–ZnS QDs on TiO2 nanowires showed only 10% lowering of efficiency after the first cycle, and any further decrease is negligible after the second cycle. Therefore, the core–shell QDs linked with TiO2 nanowires not only exhibits very good photocatalytic activity but also high stability. Similar observations have been reported earlier for CdS linked with TiO2 nanofibers,14 CdS–graphene–TiO2 nanotubes50 and graphene modified nano-Ag3PO4.51
For a better comparison of the photocatalytic activities of the experimental samples with different loading concentration of both types of QDs, the reaction kinetics were calculated based on Langmuir–Hinshelwood model, which can be expressed as;4
![]() | (1) |
![]() | (2) |
Photocatalytic degradation of dyes generally follows pseudo-first order kinetics.52 The apparent rate constant of different experimental photocatalysts for the fixed initial dye concentration and catalyst concentration are indicated in Table 1. For the bare TiO2 nanowire, the value of kapp was minimum both under UV (0.017 min−1) and visible (0.002 min−1) lights. However, after QD loading, a significant enhancement of the kapp value was observed especially under visible solar irradiation. It was observed that the photocatalytic activity is governed by QD loading onto TiO2 nanowires and also the mode of attachment between QDs and TiO2. The results show that the rate of dye degradation increases with an increase of QD loading from 2 to 10%. In explanation, QDs produce more OH˙ radicals, which are active oxidative species causing photodegradation of MB. At the same time, the QDs increase UV absorption, as well as extending the absorption to the visible range, while also helping to separate electrons and holes, thereby improving photodegradation of MB. Higher levels of loading favour the recombination of electrons and holes, leading to a lowering of photocatalytic efficiency.6 According to the experimental kinetic data, 10% loading of CdS–ZnS QDs linked with TiO2 nanowires exhibited the highest efficiency for MB degradation. Further increasing of QD loading causes aggregation of QDs as described earlier, leading to poor optical properties and photo-sensitization. The apparent kinetic rate constant was also increased in the case of QDs linked with TiO2 compared to those prepared by direct deposition. The reason behind this, the linker molecule efficiently helps to overcome the aggregation of nanowires, improving the dispersion of QDs on TiO2, resulting in enhanced interaction between QDs and TiO2 as shown earlier by SEM and TEM analysis.
| Photocatalysts | kapp (min−1) (UV) | kapp (min−1) (visible) |
|---|---|---|
| TiO2 nanowire | 0.017 | 0.002 |
| CdSZnS–MPA–TiO2 2% | 0.016 | 0.006 |
| CdSZnS–MPA–TiO2 5% | 0.034 | 0.011 |
| CdSZnS–MPA–TiO2 10% | 0.052 | 0.016 |
| CdSZnS–MPA–TiO2 20% | 0.041 | 0.013 |
| CdS–MPA–TiO2 10% | 0.027 | 0.009 |
| CdSZnS–TiO2 direct deposition | 0.020 | 0.007 |
Instead of using direct sunlight due to the large variation of UV levels,53 the photocatalytic degradation of dyes was investigated under simulated solar light (without using a UV cut off filter) for two intensities 14 and 28 mW cm−2 and variable catalyst loading concentrations. These results were then compared with the photocatalytic efficiencies observed under UV and visible light separately. Under both intensities, MB dyes did not show any degradation in the absence of the photocatalyst (Fig. 8a). The results show that the UV intensity of solar light plays an important role in the degradation of MB. At 28 mW cm−2 for 1.2 g L−1 catalyst loading, MB was decomposed completely within one hour. Increasing the UV intensity provides more energy to excite the electrons of TiO2 and QDs, creating more electron–hole pairs and also producing more OH˙ radicals, thus enhances the photocatalytic process.52 The rate constant and half life at 14 mW cm−2 were calculated as 0.024 min−1 and 28.87 min respectively (Fig. 8b). The half life under only UV and visible light were 13.3 and 43.3 min respectively. It is observed that compared to only visible light, the rate constant of the degradation reaction was relatively higher and the half life of the reaction was less under simulated sunlight, which leads to the faster degradation of MB under sunlight. In the case of photodegradation of MB under UV and visible only light, a higher catalyst loading concentration (1.2 g L−1) was used for faster photodegradation, as the increasing catalyst concentration will provide more active sites. For anatase TiO2 catalyst, a critical catalyst loading of 2 g L−1 has been described.54 At a concentration lower than this value, kapp increases with increasing catalyst concentration. Some research groups have reported catalyst loading concentrations of 1.2 g L−1 or higher for the decomposition of similar initial concentration of dyes.39,51,55
In addition, the photocatalytic degradation of MB was also studied with changing catalyst (CdSZnS–MPA–TiO2 nanowires) loading concentration under stimulated solar light as shown in Fig. 8b. For the lowest concentration (0.3 g L−1), the apparent rate concentration was 0.012 min−1, and 70% of dye was decomposed in the first 2 hours. By further increasing the concentration to 0.6 g L−1, 100% dye decomposition was observed in the first 2 hours with a kapp 0.033 min−1. For the highest dosage 1.2 g L−1, the decomposition was very fast with a rate constant 0.047 min−1. In considering the process economy, 0.6 g L−1 would be an optimum loading concentration as it shows a high photocatalytic degradation of MB dye in a reasonable time period.
Fig. 9 provides the OH˙ production by the experimental photocatalyst (CdSZnS–MPA–TiO2 nanowires) with terephthalic acid as a fluorescent probe. No peak was observed in the absence of light or photocatalyst samples. But in the presence of light, a gradual increase in PL intensity at about 425 nm was observed with increasing irradiation time (from 5 to 30 min). This has been shown to be from the formation of highly fluorescent product, 2-hydroxyterephthalic acid from the reaction of terephthalic acid and OH˙.51,56 Higher intensities indicate higher amounts of OH˙ production, which is the major species responsible for the photocatalytic degradation of MB.
A proposed mechanism of excitation and charge transfer process between the core–shell CdS–ZnS QDs and TiO2 is shown in Fig. 10. In this work, we fabricated CdS–ZnS QDs for broad absorption and efficient carrier extraction in TiO2 assemblies. Due to the position of the conduction band (CB) and valence band (VB) of both QDs, the optimal CB and VB edges are located in the core CdS QDs. The electron–hole recombination rate is much slower in the core–shell QDs than that of the core QDs because of instability of the core.57 As the CB edge of TiO2 is more positive than this optimal CB of the core–shell QDs, the photogenerated electrons are transferred to the CB of TiO2, leading to a higher concentration of electrons. Meanwhile, the hole generated on the optimal VB of QDs remains instead of being transferred to the VB of TiO2, as this optimal VB is more cathodic than that of TiO2.58
![]() | ||
| Fig. 10 Schematic description of the charge transfer and separation between CdS–ZnS and TiO2 in the CdS–ZnS QDs linked with TiO2 nanowires under visible irradiation. | ||
The electrons (e−) accumulated at the CB of TiO2 are scavenged by dissolved oxygen molecules in water to yield superoxide radial anions (O2−˙) (eqn (4)), yielding hydroperoxy radicals HO2˙ on protonation (eqn (6)), and finally hydroxyl radicals OH˙ (eqn (7)). During this reaction, H2O2 is also formed which can be further reduced to OH˙ (eqn (8)). Meanwhile, the holes on the optimal VB of the core–shell QDs can potentially react with surface hydroxyl groups or physisorbed water molecules to form OH˙ radicals (eqn (5)). The highly reactive OH˙ radicals are strong oxidising agents which can decompose organic pollutants.46,47 The proposed mechanism illustrated in Fig. 10 can be summarized as the following equations:
| (CdSZnS–TiO2) + hν → TiO2(eCB−) + CdSZnS(hVB+) | (3) |
| TiO2(eCB−) + O2 → TiO2 + O2−˙ | (4) |
| CdSZnS(hVB+) + OH− → CdSZnS + OH˙ | (5) |
| O2−˙ + H2O → HO2˙ + OH− | (6) |
| HO2˙ + H2O → OH˙ + H2O2 | (7) |
| H2O2 → 2OH˙ | (8) |
| Methylene blue + OH˙ → degradation products | (9) |
| This journal is © The Royal Society of Chemistry 2015 |