Q. Chang†
*a,
X. Meng†a,
S. L. Hu*a,
F. Zhangb and
J. L. Yangac
aSchool of Materials Science and Engineering, North University of China, Xueyuan Road 3, Taiyuan 030051, China. E-mail: changneu@gmail.com; hsliang@yeah.net; Fax: +86 351 3559638; Tel: +86 351 3559638
bJinzhong Institute of Quality and Technical Supervision Inspection & Measurement, Yuci 030600, China
cState Key Laboratory of New Ceramics and Fine Processing, Tsinghua University, Beijing 100084, China
First published on 12th June 2017
In this study, a new hydroxyapatite/N-doped carbon dots/Ag3PO4 (HA/N-CDs/Ag3PO4) composite was prepared by a facile hydrothermal approach and in situ ion-exchange reaction method. The photocatalytic performance of the as-prepared samples was investigated by the degradation of methylene blue (MB) under visible light irradiation. It was found that the HA/N-CDs/Ag3PO4 composite exhibited much higher photocatalytic activity and stability compared with HA/N-CDs and HA/Ag3PO4. In addition, the effect of the amount of silver loading on the photocatalytic activity of the composite was evaluated. The experimental results showed that a higher silver loading amount led to a decrease of both the UV-Vis absorption and photocatalytic performance. A suitable content of silver loading produced the highest photocatalytic activity. The substantial improvement in the photocatalytic performance of the composite can be attributed to the synergetic effects of HA support, CDs and the formed Ag3PO4, which led to an increase of active sites, suppression of the electron–hole recombination, and the stability improvement of Ag3PO4. The HA/N-CDs/Ag3PO4 photocatalyst synthesized via a cost-effective route is a promising candidate in organics removal.
Hydroxyapatite (HA) is well-known as an inorganic biomaterial due to its excellent bioactivity and biocompatibility.9 In recent years, it has also been demonstrated to display remarkable properties as a catalyst support, since it possesses very unique properties, including rich polar groups (OH−, PO43−), good affinity, high stability and low cost. For instance, the composites of metal (Ru, Au, Co) supported on HA10,11 and semiconductor loaded on HA,12–15 have been prepared and found to exhibit enhanced catalytic performance.
Carbon dots (CDs), a novel nanocarbon material, have drawn intensive interest due to their excellent properties, such as low cost, low toxicity, easy functionalization and so on.16,17 Given their electron-accepting/transfer properties, CDs have been proven to be a potential photocatalyst.18–20 Meanwhile, it has been demonstrated that introducing CDs into semiconductors could remarkably enhance the photocatalytic activities of the composites.21–25 The tunable photocatalytic properties of CDs have also been widely investigated in our research group.26–31 More recently, the present authors developed a hydroxyapatite supported N-doped CDs composite to solve the aggregation and non-recyclability of CDs.32 However, the high photocatalytic efficiency and visible light utilization still remain a challenge. It is necessary to develop new and efficient photocatalysts.
Ag3PO4, as one of the semiconductor photocatalysts, has been reported to show excellent photocatalytic activity.33 However, owing to the solubility and unstable property under light irradiation,34,35 plus the consumption of noble metal, the photocatalytic application of Ag3PO4 is strongly limited. To solve the limitations of Ag3PO4, hybrid photocatalysts have been proposed.13,14,22,36–40 Among them, Zhang et al.22 reported that coupling Ag3PO4 with CDs was an effective strategy to improve the stability of Ag3PO4, since the dissolution of Ag3PO4 could be impeded by CDs. Hong et al.13 and Chai et al.14 also pointed out hydroxyapatite supported Ag3PO4 prepared via in situ ion-exchange method could effectively reduce the cost and improve the photocatalytic activity of the composite. Considering the unique characteristics of CDs and HA, coupling them with Ag3PO4 to form a ternary HA/CDs/Ag3PO4 composite is expected to improve both the photocatalytic efficiency and stability, as well as reduce the cost. The purpose of this investigation was, therefore, to synthesize HA/N-CDs/Ag3PO4 composite in an attempt to develop a new hybrid photocatalyst with improved photocatalytic efficiency and stability via a cost-effective route, evaluate the microstructure and photocatalytic performance of the composites, and identify the underlying mechanisms.
The photocatalytic performance of the prepared samples was evaluated by the photocatalytic degradation of MB aqueous solution under visible-light irradiation at ambient temperature. 0.04 g photocatalyst was suspended in 40 mL of MB aqueous solution (20 mg L−1). The mixed solution was treated by ultrasonication for 10 min, and then stirred under the dark condition for 1 h to ensure the adsorption–desorption equilibrium before visible-light irradiation. The reaction solution was subsequently positioned 20 cm away from the reactor and irradiated under continuous stirring. A 300 W Xe arc lamp with an UV-cutoff filter (λ < 420 nm) was used as a visible light source. After irradiation for some time, about 2 mL of the reaction solution was withdrawn and centrifuged. The concentration of MB was determined by measuring the absorbance peak at 664 nm via a UV-Vis spectrophotometer. For comparison, blank experiment was also performed in the absence of photocatalyst.
To investigate the stability of heterostructured HA/N-CDs/Ag3PO4 composite, consecutive three times recycling experiments were carried out as follows. After one cycle, the HA/N-CDs/Ag3PO4 powders were treated with ultrasonication, collected by centrifugation, and washed by distilled water three times. After dried at 60 °C for 12 h in a vacuum oven, the recycled HA/N-CDs/Ag3PO4 powders were collected and reused in the next cycle.
Fig. 3 shows the TEM images of HA, N-CDs, Ag3PO4 and HA/N-CDs/Ag3PO4. It is seen that HA exhibited rod-like morphology (Fig. 3A). N-CDs were dispersed uniformly on TEM grid (Fig. 3B) and presented a round shape with diameters ranging from 1 to 5 nm. And nanosized Ag3PO4 particles were observed (Fig. 3C). For HA/N-CDs/Ag3PO4, it can be seen from Fig. 3D that Ag3PO4 particles with size of 5–10 nm dispersed on the surface of HA. The size of Ag3PO4 particles was smaller than bare Ag3PO4, implying the in situ ion-exchange method could effectively reduce the size of Ag3PO4 particles. As can be seen from the corresponding HRTEM image (Fig. 3E), CDs were found. In addition, the HRTEM image clearly displays the lattice spacing of 0.279 nm, 0.267 nm and 0.204 nm, corresponding to the HA (112) plane, Ag3PO4 (210) plane and CDs (101) plane. The EDS pattern of HA/N-CDs/Ag3PO4 was also shown in Fig. 3F. The characteristic signals of Ca, P and O were derived from HA, and signals of Ag were derived from Ag3PO4. These results suggested that the HA/N-CDs/Ag3PO4 composite was successfully obtained.
Fig. 3 TEM images (A–D) of HA, N-CDs, Ag3PO4, HA/N-CDs/Ag3PO4, HRTEM image (E) and EDS analysis (F) of HA/N-CDs/Ag3PO4. |
The XPS was also evaluated to further investigate the elemental compositions and chemical states of the samples. Fig. 4A shows the high-resolution C1s XPS spectra of HA/N-CDs/Ag3PO4-a in comparison to HA/Ag3PO4 (with the same theoretical molar ratio (0.15) of Ag3PO4 to HA). It is seen that the main C1s peaks at about 284.8 eV and 288.8 eV for HA/Ag3PO4 were observed although no CDs were added. This is because CO2 inevitably was adsorbed and incorporated into the HA structure during the preparation. After the introduction of CDs, it was observed that the two peaks for HA/N-CDs/Ag3PO4 became stronger. Fig. 4B shows the high-resolution XPS spectra of O1s. It can be seen that the peak at 531 eV of HA/N-CDs/Ag3PO4-a is stronger than that of HA/Ag3PO4. This is also attributed to the presence of CDs which possess a certain content of O-containing groups such as C–O and CO.29 The high-resolution XPS spectra of Ag3d (Fig. 4C) show the binding energy of the Ag3d5/2 and Ag3d3/2 peaks at 368 eV and 374 eV. It is interesting to found that the two peaks for HA/N-CDs/Ag3PO4-a became weaker than that of HA/Ag3PO4. The reduction of the peak intensity was associated with the CDs shell on the surface of Ag3PO4 that obstructed the detection. These above results fully confirmed that the HA/N-CDs/Ag3PO4 composite was well achieved.
Fig. 5 shows the UV-Vis absorption spectra of HA/N-CDs, HA/Ag3PO4 and HA/N-CDs/Ag3PO4-a. It is seen that the absorption intensity of HA/N-CDs was weakest. For HA/Ag3PO4 obtained via ion-exchange method, it was observed a red shift in the absorption edge and the increased absorption intensity. This is attributed to the narrow band gap of Ag3PO4 (2.5 eV), leading to a wider absorption in the visible-light region. Compared to HA/N-CDs and HA/Ag3PO4, the visible-light absorption of HA/N-CDs/Ag3PO4-a was further enhanced. The stronger absorption is beneficial for improving photocatalytic performance.
Fig. 6 (A) Photocatalytic activities of HA/N-CDs, HA/Ag3PO4 and HA/N-CDs/Ag3PO4-a for MB degradation under visible-light irradiation, and (B) plots of ln(C/C0) versus irradiation time (t). |
It is seen that 50 min was taken to degrade 90% of MB for HA/N-CDs, which was in agreement with our previous result.32 And 25 min was taken to degrade about 92% of MB for HA/Ag3PO4. The improvement of the photocatalytic activity for HA/Ag3PO4 was associated with the good absorption of Ag3PO4 in the visible-light region (Fig. 5). It should be noted here that the photocatalytic activity of HA/Ag3PO4 in the present study was much better than that reported by Hong et al.13 (68% of MB was degraded after 20 min irradiation), which could be attributed to the characteristics of HA support. The obtained HA in our study had high purity and crystallization (Fig. 2). In particular, the rod-like nanosized HA exhibited no aggregation (Fig. 3A). The good dispersibility of HA could be favorable for the synthesis of uniform Ag3PO4 on its surface. Compared with HA/N-CDs and HA/Ag3PO4, a significant result observed in this study was that HA/N-CDs/Ag3PO4-a exhibited the highest photocatalytic activity, and 98% of MB was degraded after 20 min irradiation. Simultaneously, the characteristic absorption of MB (λmax = 664 nm) (inset in Fig. 6A) was observed to decrease with increasing the irradiation time, implying that MB decomposed.
To better investigate the photocatalytic performance of as-prepared samples, a kinetic study via using pseudo-first-order kinetics was evaluated, as shown in Fig. 6B. The degradation rate of MB on HA/N-CDs/Ag3PO4-a was calculated to 0.1782 min−1, which was about 4.2 times of HA/N-CDs (0.04217 min−1) and 1.8 times of HA/Ag3PO4 (0.09635 min−1). The above results strongly suggested that the ternary HA/N-CDs/Ag3PO4 composite can be used as a new and effective visible-light-responsive photocatalyst.
Fig. 7 (A) XRD patterns of HA/N-CDs/Ag3PO4 with different silver loading amount, (B) UV/Vis absorption spectra, (C) photocatalytic activities, and (D) plots of ln(C/C0) versus irradiation time (t). |
Fig. 7B and C show the UV-Vis absorption spectra and photocatalytic activities of the samples. With the same trend as that of the XRD intensity, both the absorption in the whole visible-light and the photocatalytic performance increased first and then decreased with increasing the content of silver loading. HA/N-CDs/Ag3PO4-c exhibited the widest and strongest absorption and showed the highest photocatalytic activity. 98% of MB was degraded after 6 min irradiation. The characteristic absorption of MB (λmax = 664 nm) (inset in Fig. 7C) almost disappeared after 6 min irradiation. Moreover, the decomposition rate of MB was also calculated, as shown in Fig. 7D. It is seen that the rate of HA/N-CDs/Ag3PO4-c reached the maximum value of 0.5850 min−1.
These results demonstrated that further increase of silver loading amount (HA/N-CDs/Ag3PO4-d) resulted in the decrease of both the UV-Vis absorption and photocatalytic performance. This was related with two potential reasons. First, the photocorrosion of Ag3PO4 could happen due to its lower crystallization for HA/N-CDs/Ag3PO4-d, as revealed by XRD patterns (Fig. 7A). Second, CDs which played key role in protecting dissolution of Ag3PO4 were covered by the excess Ag3PO4. Therefore, further increase of the content of silver loading led to a decrease of both the absorption property and photocatalytic activity.
Furthermore, the stability of a photocatalyst is needed for its far-reaching applications. In this study, recycle experiments of MB degradation on the sample HA/N-CDs/Ag3PO4-c with the best photocatalytic performance was investigated and the corresponding result is shown in Fig. 8. It can be clearly seen that although the photocatalytic activity showed slight decrease, the degradation of MB was maintained at 95% after three repeated cycles, suggesting high stability of HA/N-CDs/Ag3PO4.
First, the photocatalytic activity is inherently determined by its composition. Although Ag3PO4 is an efficient visible-light photocatalyst, it possesses certain solubility in aqueous solution and has relative larger particle size.14 The two factors intrinsically weaken the photocatalytic activity. In this study, CDs dispersed on the surface of the composite that could effectively prevent the dissolution of Ag3PO4 so as to improve the photocatalytic activity and the stability of the composite. Moreover, CDs also possess the property of the broadband optical absorption. Therefore, compared with HA/N-CDs and HA/Ag3PO4, HA/N-CDs/Ag3PO4 composite exhibited a higher absorption intensity in the visible region (Fig. 5).
Second, the activity of a photocatalyst is also dependent on its microstructure. As revealed by the TEM results (Fig. 3), in this study, HA nanorods with tens of nanometers in length were obtained. CDs and Ag3PO4 were homogeneously distributed on the HA surface. The obtained strawberry-like structure could give a high surface area that can strengthen light harvesting. In addition, the size of Ag3PO4 was in the range of 5–10 nm, which is also beneficial for the enhanced photocatalytic activity. Importantly, the conjugation between HA and N-CDs was due to the interaction between hydroxyl on the surface of HA and surface groups of N-CDs,32 which could lead to a good interfacial bonding. What is more, Ag3PO4 prepared via in situ ion-exchange method intrinsically had an appropriate bonding between HA. Therefore, a good connection between them was obtained, which could be the potential transfer channel of the photogenerated electrons and holes, giving rise to a reduction of the recombination. So the photocatalytic performance of the ternary composite was remarkably improved.
Third, a key factor that affects the activity of the photocatalysts is the abundant surface active sites which depend on the separation and transfer of the photogenerated electrons (e−) and holes (h+). For Ag3PO4, the photogenerated electrons tend to reduce Ag+ to Ag rather than form superoxide radical in the absence of electron acceptors since the potential of the conduction band (CB) is more positive than the reduction potential of O2 (−0.33 eV vs. NHE).14 However, the superoxide radicals (˙O2−) are the important reactive species for decomposing organic molecules. In the present study, we examined the main oxidative centers (˙O2− and ˙OH) in the HA/Ag3PO4 and HA/N-CDs/Ag3PO4 composites by a spin trapping method, as shown in Fig. 9. As seen from the Fig. 9A, the peaks of the DMPO–˙O2− adducts for HA/Ag3PO4 were observed under visible light irradiation for 5 min, which was in agreement with the literature reported by Chai et al.14 In comparison to HA/Ag3PO4, a significant result was observed that the ESR signal for HA/N-CDs/Ag3PO4 composite was much stronger, implying more ˙O2− radicals were formed. For the ESR spectra of ˙OH trapped by DMPO (Fig. 9B), it can also be seen that a much stronger ESR signal was produced on the HA/N-CDs/Ag3PO4 than on the HA/Ag3PO4, with the same trend as that of ESR spectra of ˙O2−. The results proved the formation of the more oxidizing active sites for the ternary composite in the photodegradation process. The more the active sites, the higher the photocatalytic degradation of organic molecules. The above results were well consistent with the photoactivity results (Fig. 6). This could be understood as follows.
Fig. 10 illustrates the separation and transfer behaviors of photogenerated electrons and holes of the ternary composite. Under visible-light irradiation, photogenerated electrons and holes of Ag3PO4 and CDs were produced. It is known that CDs could act as both the electron acceptors and donors. As electron acceptors, they can trap photogenerated electrons from Ag3PO4, thus effectively suppressing the recombination of the photogenerated electron/hole pairs and impeding the photocorrosion of Ag3PO4. Meanwhile, the photogenerated electrons could also migrate to HA due to its storage property of electrons,15 leading to the separation of electron–hole pairs. The electrons accumulated on CDs and HA could adsorb the O2 in solution to form ˙O2− (Fig. 9A), which could degrade the MB. The electrons that created the superoxide radicals resulted in another kind of significant oxidizing active sites of photogenerated holes. In addition, the higher quantity of holes (h+) led to the increase of ˙OH (Fig. 9B), which could significantly improve the photocatalytic activity. As a consequence, the heterostructured HA/N-CDs/Ag3PO4 photocatalyst exhibited excellent photocatalytic performance.
Footnote |
† These authors contributed equally. |
This journal is © The Royal Society of Chemistry 2017 |