Skip to main content
PMC home page
Frontiers in Chemistry logoLink to Frontiers in Chemistry
. 2018 Oct 2;6:393. doi: 10.3389/fchem.2018.00393

BiOCl Decorated NaNbO3 Nanocubes: A Novel p-n Heterojunction Photocatalyst With Improved Activity for Ofloxacin Degradation

Jingjing Xu 1,*, Bingbing Feng 1, Ying Wang 1, Yadi Qi 1, Junfeng Niu 2, Mindong Chen 1
PMCID: PMC6175997  PMID: 30333968

Abstract

BiOCl/NaNbO3 p-n heterojunction photocatalysts with significantly improved photocatalytic performance were fabricated by a facile in-situ growth method. The obtained BiOCl/NaNbO3 samples were characterized by UV-vis absorption spectroscopy, scanning electron microscopy (SEM), X-ray diffraction (XRD), photocurrent (PC) and photoluminescence spectroscopy (PL). The photocatalytic activity of the BiOCl/NaNbO3 samples was investigated by the degradation of a typical antibiotic Ofloxacin (OFX). The experimental results showed that BiOCl/NaNbO3 composites exhibited much higher photocatalytic activity for OFX degradation compared to pure NaNbO3 and BiOCl. The degradation percent of OFX reached 90% within 60 min, and the apparent rate constant was about 8 times as that of pure NaNbO3 and BiOCl. The improved activity can be attributed to the formation of p-n junction between NaNbO3 and BiOCl. The formed p-n junction facilitated the separation of photogenerated holes and electrons, thereby enhancing photocatalytic activity. In addition, the composite photocatalyst showed satisfactory stability for the degradation of OFX. Due to the simple synthesis process, high photocatalytic activity, and the good recyclability of these composite photocatalysts, the results of this study would provide a good example for the rational design of other highly efficient heterojunction photocatalytic materials.

Keywords: photocatalysis, BiOCl, NaNbO3, p–n junction, ofloxacin

Introduction

The problem of water pollution has attracted increasing attention worldwide due to many toxic pollutants continue to enter into our water bodies (Ao et al., 2016b; Li et al., 2018; Yuan et al., 2018). As a green and sustainable technology, semiconductor photocatalysis can completely eliminate most pollutants in water and air (Zhang et al., 2016, 2017a,b; Chen et al., 2018; Guo et al., 2018; He et al., 2018; Yang et al., 2018). The contaminants are degraded by hydroxyl radical or other free radicals which are produced in the process after the absorption of light (Li et al., 2015; Cao et al., 2016; Xu et al., 2016; Yu et al., 2016; Zhang and Xiao, 2017; Han et al., 2018; Zhong et al., 2018). There are many semiconductors (such as oxides, sulfides, nitrates and silver based compounds etc.) can be served as photocatalysts to induce the degradation of pollutants.

In recent years, NaNbO3 has attracted much attention due to its unique properties of nonlinear optics, ferroelectric, ionic conduction, photorefractive and photocatalytic properties (Katsumata et al., 2010; Lv et al., 2010; Li et al., 2012a, 2013; Fan et al., 2015; Qian et al., 2018). Because NaNbO3 is a typical n type semiconductor with unique crystal [NbO6] angle eight-hedral crystal structure, it has the advantage of relative high transfer efficiency of electrons during the photocatalytic process (Shi et al., 2014b; Song et al., 2015). Recent studies have shown that NaNbO3 can be used as an efficient photocatalyst for the evolution of H2 and the reduction of CO2 (Li et al., 2012b, 2014). In addition, NaNbO3 also shows the ability for the decomposition of organic pollutants (Li et al., 2008; Li, 2010; Chen et al., 2014). However, because NaNbO3 has a large band-gap, it cannot be used as a visible light responsive photocatalyst. Various experiments have shown that forming heterojunction with other semiconductor materials was a promising way to improve the photocatalytic activity of NaNbO3. For example, an effective composite photocatalyst NaNbO3/WO3 has been proved to has stronger dye degradation activity compared with the corresponding single component (Shifu et al., 2013). Moreover, other NaNbO3 based composite photocatalysts, such as AgO2/NaNbO3 (Zhang et al., 2017), Pt/NaNbO3 (Liu et al., 2016) and CdS/NaNbO3 (Kumar et al., 2014), were also successfully prepared for photocatalytic degradation of pollutants.

On the other hand, although BiOCl (a typical p-type oxyhalide semiconductor) has been extensively investigated in the field of photocatalysis (Ye et al., 2014; Ao et al., 2016a; Hu et al., 2016; Mao et al., 2016; Ma Y. C. et al., 2016; Wang et al., 2018). However, the recombination rate of photogenerated charges in pure phase of BiOCl is high, resulting in its limited photocatalytic activity under UV light. It has recently been found that the photocatalytic activity of BiOCl can be promoted through the formation of p-n junctions with n type semiconductors (Rajeshwar et al., 2001; Wang et al., 2012; Fang et al., 2016). The enhanced activity can be ascribed to the fact that the internal electric field at the p-n junction interface improved the separation and transfer of photo-generated charges (Yan et al., 2017). However, as far as we know, the preparation and activity of BiOCl/NaNbO3 p-n heterojunction photocatalyst have not been studied yet.

In the present work, we constructed a new type of p-n heterojunction photocatalyst (BiOCl/NaNbO3) by a simple in situ growth method. Compared with pure BiOCl and NaNbO3, the composite has better photocatalytic activity for the degradation of ofloxacin (OFX). The experimental results proved that the p-n junctions formed between BiOCl/NaNbO3 composites promote the transfer and separation of photogenerated electron-hole pairs, thus enhancing the photocatalytic activity.

Experimental

Synthesis of NaNbO3 cubes

All the reagents and materials used in this experiment were analytical grades. All of them were purchased from China pharmaceutical chemical reagents Co., Ltd. NaNbO3 was directly synthesized by hydrothermal method described as following. 2 g Nb2O5 was added to the 120 mL NaOH solution (10 M) and stirred for 120 min before the suspension was transferred to the 200 ml Teflon-lined stainless steel autoclave. The reaction kettle was kept at 150°C for 48 h. Subsequently, the autoclave was cooled to room temperature naturally after the reaction. Then remove the reactor and precipitate it naturally, pour the supernatant out of the precipitate and centrifugate, then wash it with deionized water and ethanol for 3–5 times. Finally, the product was dried for 12 h in a vacuum oven at 60°C.

Synthesis of BiOCl/NaNbO3 p–n junction photocatalysts

BiOCl/NaNbO3 heterostructures were prepared by a simple in-situ growth method. A certain amount of Bi(NO3)3.5H2O was added to 300 mL of ultrapure water and stirred for 1 h to form solution A. Meanwhile, NaNbO3 powder was dispersed in 80 mL ultrapure water and sonicated for 30 min to form solution B. A certain amount of KCl was added to 60 mL ultrapure water to form solution C. Finally, B and C were slowly added to A under rapid stirring. Afterwards, the stirring was continued for 24 h. The product was then filtered and thoroughly washed with distilled water and ethanol before it was dried at 60°C for 24 h. By Changing the amount of Bi(NO3)3·5H2O and KCl added, NaNbO3/BiOCl composites with different theoretical BiOCl mass ratios of 10, 25, 75, and 100% (expressed as BN-1, BN-2, BN-3, and BN-4) were produced. In order to facilitate comparison, pure BIOCl samples are also prepared in the same way, that is to say, no NaNbO3 is added in the process of making composite samples.

Characterization of photocatalysts

The results of X ray diffraction (XRD) scanning of pure BiOCl, NaNbO3 and BiOCl/NaNbO3 were recorded by Shimadzu XRD 6100 X-ray diffractometer. The morphology and microstructure of the samples were characterized by scanning electron microscopy (SEM, Hitach S-4800). The band gap (Eg) of the sample was measured by UV-vis absorption spectroscopy at 200~800 nm at room temperature, and the integrated ball attachment was installed on the ultraviolet visible spectrophotometer (UV-3600). Photocurrent (PC) and mott-Schottky (MS) were carried out on the traditional three electrode system (the electrochemical workstation of CHI-660D Chenhua chemical equipment company in Shanghai, China). The contrast electrode and the reference electrode are platinum electrodes and Ag/AgCl electrodes respectively.

Photocatalytic activity experiments

The experimental vessel is a double-layer quartz beaker with cooling water circulation system for photocatalytic reaction. During the experiment, the temperature of the solution can be maintained at about 25 °C, so as to reduce the influence of temperature on the experiment. The light source used in the photocatalytic process is a 300 W xenon lamp(200 nm < λ < 400 nm), and before irradiation, 25 mg photocatalyst was added to 50 mL OFX solution (5 mg/L). The suspension was stirred magnetically in the dark for 30 min to achieve adsorption/desorption equilibrium between photocatalysts and OFX. During the photocatalytic process, a certain suspension was sampled at the prescribed time intervals. The sampled suspension was centrifuged before the determination of OFX concentration.

Results and discussion

Characterizations

The XRD diagrams of pure BiOCl, NaNbO3 and BiOCl/NaNbO3 composites were shown in Figure 1. It can be seen that there are seven different diffraction peaks, which can be indexed to tetragonal BiOCl (JCPDS card number 01-0600) (Ma W. et al., 2016). Sharp and narrow diffraction peaks indicate good crystallinity for pure BiOCl. From the pattern of pure NaNbO3, several main diffraction peaks can be seen at 22.7, 32.5, 46.4, 52.7, 58.1, and 68.11° corresponding to (001), (110), (002), (021), (112), and (022) planes of NaNbO3 orthorhombic phases (JCPDS card number 33-1270) (Saito and Kudo, 2013). The diffraction peaks of pure BiOCl and NaNbO3 and the diffraction peaks of heterostructure BiOCl/NaNbO3 composites can be clearly observed by XRD diagram. In addition, when the mass ratio of BiOCl to NaNbO3 increases from 10 to 100%, the diffraction peak intensity of BiOCl increases and the corresponding NaNbO3 peak intensity decreases. Furthermore, when BiOCl grows on NaNbO3, its diffraction peak is wider than that of pure BiOCl. This phenomenon indicates that BiOCl on the surface of NaNbO3 cube has smaller particle size. The result indicates that the addition of NaNbO3 can effectively inhibit the growth of BiOCl (Shang et al., 2009). XRD showed that the samples were clean and had no other phase of impurity, so the composites were basically composed of BiOCl and NaNbO3.

Figure 1.

Figure 1

Open in a new tab

XRD patterns of BiOCl, NaNbO3, and BiOCl/NaNbO3 composites with different BiOCl contents.

The morphology and structure of BiOCl, NaNbO3, and BiOCl/NaNbO3 composites can be clearly seen by SEM characterization. The SEM image of pure BiOCl is displayed in Figure 2a. As can be seen from the graph, pure BiOCl is composed of regular, square like nano plates. At the same time, we can see that the synthesized NaNbO3 has irregular cubic shape and smooth surface in Figure 2b. A typical SEM image of the BN-3 composite is shown in Figure 2c. It can be seen that NaNbO3 cubes are anchored by BiOCl nanosheets which are thiner and smaller than pure BiOCl. During the in-sith growth process, the NaNbO3 particles played a role of heterogeneity and inhibited the growth of BiOCl to lager ones. After analyzing the SEM image, the conclusion is in good agreement with the previous XRD analysis. BiOCl and NaNbO3 form p-n junctions at the interface because of the close contact between BiOCl and NaNbO3. This improves the carrier transport rate and separation efficiency in photocatalysis and helps to improve the activity.

Figure 2.

Figure 2

Open in a new tab

SEM images of pure BiOCl (a), NaNbO3 (b) and BN-3 (c).

The optical properties of the samples have a great influence on the utilization of sunlight. Therefore, UV-DRS for pure BiOCl, NaNbO3 and BiOCl/NaNbO3 composites are investigated. As we can see from Figure 3, the absorbance threshold of NaNbO3 and pure BiOCl are at about 400 and 380 nm, respectively. The band-gap of photocatalysts can be obtained from the following equation:

Figure 3.

Figure 3

Open in a new tab

UV-vis absorption spectra of BiOCl, NaNbO3 and BN-3.

Eg=1240/λ,

where Eg is the band-gap energy and λ is the cut off wavelength. Therefore, the band gaps of NaNbO3 and BiOCl prepared were 3.10 and 3.26 eV, respectively, which are similar to those reported previously (Shi et al., 2014a; Ma W. et al., 2016). It can also be seen from Figure 3 that BiOCl/NaNbO3 exhibits higher UV absoption performance compared to pure BiOCl. Furthermore, the band edge of BiOCl/NaNbO3 exhibits a little red shift compared to pure BiOCl.

Through the band structure of the catalyst, we further explore the way of carrier transfer. The type and surface potential of NaNbO3 and BiOCl semiconductors are determined by the Mott-Schottky plots. The positive tangent in the graph indicates that the sample is n type semiconductor, while the negative tangent in the graph indicates that the sample is p type semiconductor (Kuang et al., 2015). The results shown in Figures 4A,B show that BiOCl and NaNbO3 are p-type and n-type semiconductors, respectively. In addition, the flat potential (relative to Ag/AgCl) of BiOCl and NaNbO3 are 2.30 V and −0.70 V respectively through the intersection point between tangent and abscissa. According to the following equation, the potential (relative to Ag/AgCl) can be converted to a normal hydrogen electrode (NHE). (1) (Zhou et al., 2017; Liu et al., 2018):

Figure 4.

Figure 4

Open in a new tab

The Mott-Schottky plots of (A) NaNbO3 and (B) BiOCl.

ENHE=EAg/AgCl+EAg/AgCl0

where EAg/AgCl0 = 0.197 V. In particular, the maximum of the valence band (VB) is about 0.1 V lower than the flat potential of the p-type semiconductor; the minimum value of the conduction band (CB) is about 0.1 V higher than the flat potential of the n-type semiconductor (Liu et al., 2017b). Therefore, the VB position of BiOCl and the CB position of NaNbO3 are 2.60 and −0.60 V (vs. NHE), respectively. The Eg of BiOCl and NaNbO3 were 3.26 and 3.10, respectively. Therefore, according to Eg. (2) (Liu et al., 2017a):

Eg=EVB-ECB

the position of CB and VB for BiOCl and NaNbO3 are −0.66 and 2.50 V, respectively.

Photocatalytic activity

The photocatalytic activity of BiOCl/NaNbO3 composites with p-n junctions is mainly studied on the degradation of OFX under UV irradiation. As shown in Figure 5A, In the presence of NaNbO3 or BiOCl, about 20% OFX are decomposed within 60 min. It can also be seen that all BiOCl/NaNbO3 composites exhibit significantly higher photocatalytic activity than that of pure BiOCl and NaNbO3. In addition, it was found that the mass ratio of BiOCl has a significant effect on the activity of BiOCl/NaNbO3 composites. Specifically, the activity increase gradually when the BiOCl content is increased from 10 to 75%. When the content of BiOCl is further increased to 100%, the activity of the sample begin to decrease. Therefore, sample BN-3 with BiOCl mass ratio of 75% exhibites the highest activity (the degradation percent of OFX is about 90% after 60 min irradiation). The time evolution of the OFX solution spectra in the degradation process by BN-3 were measured and are shown in Figure 5B. The absorption peak of OFX decreases as the increase of irradiation time and reaches the minimum at 60 min.

Figure 5.

Figure 5

Open in a new tab

(A) Photocatalytic activities of NaNbO3, BiOCl and BiOCl/NaNbO3 composites for the degradation of OFX (5 mg/L) under UV light irradiation (200 nm < λ < 400 nm), (B) UV spectral changes of OFX in aqueous BN-3 composites dispersions as a function of irradiation time, (C) The kinetics of OFX degradation, and (D) The degradation rateconstants.

It has also been found that the photocatalytic degradation of OFX follows pseudo-first order kinetic calculated from the following formula (as shown in Figure 5C):

-ln(Ct/C0)=kt

The obtained k of OFX removal rate of pure BiOCl, NaNbO3 and BiOCl /NaNbO3 composites can be calculated by this formula. In Figure 5D, it is more clear to see that the kinetic constants of BiOCl, NaNbO3, BN-1, BN-2, BN-3, and BN-4 are 0.0021, 0.002, 0.0071, 0.0094, 0.016, and 0.011 min−1, respectively. Therefore, compared with the single phase BiOCl and NaNbO3, the BiOCl/NaNbO3 composite can promote the separation of the electron-hole pairs on the interface, thus promoting the enhancement of the photocatalytic activity.

The stability of one photocatalyst is very important to the practical application. Therefore, the recycle experiments are carried out for BN-3. As shown in Figure 6, the photocatalytic performance of the catalyst has only slight loss after four cycles of reutilization of the photocatalyst. This experimental phenomenon indicates that the photocatalyst is stable to the photodegradation of OFX. The experimental results show that the photocatalytic degradation of organic pollutants by the prepared BiOCl/NaNbO3 composites is stable, and it is of great significance for the practical application of the catalyst.

Figure 6.

Figure 6

Open in a new tab

Cyclic operation of BN-3 under UV light.

Photocatalytic mechanism

The interfacial charge transfer kinetics between BiOCl and NaNbO3 can be further elucidated by photocurrent measurements. Figure 7 shows the photocurrent-time curves of the BiOCl, NaNbO3, and BN-3 composites under an on/off cycle of intermittent UV irradiation. As shown in Figure 7, BN-3 composite exhibits much higher photocurrent than that of pure BiOCl and NaNbO3. Therefore, the BN-3 can transfer and separate photogenerated electron hole pairs more efficiently under ultraviolet light irradiation. In addition, the photoluminescence (PL) spectra of pure BiOCl, NaNbO3 and BiOCl/NaNbO3 composite samples were tested to determine the separation efficiency of photo-generated charges. The excitation wavelength used in the test is 285 nm. In Figure 8, it is found that pure NaNbO3 is the strongest relative to other sample emission peaks within the range of 350–550 nm. For pure BiOCl samples, their emission peaks are relatively weak relative to pure NaNbO3. The PL luminescence strength of BN-3 composites is the lowest in the three samples. The results show that the combination of pure BiOCl and NaNbO3 can effectively inhibit the recombination of electron hole pairs. The results are in good agreement with the measurement results of photocurrent.

Figure 7.

Figure 7

Open in a new tab

Transient photocurrent responses for NaNbO3, BiOCl, and BN-3 composite.

Figure 8.

Figure 8

Open in a new tab

PL emission spectra of NaNbO3, BiOCl, and BN-3 composite.

In order to study the degradation mechanism, the main active species produced in the degradation process were determined. Therefore, three radical scavengers such as isopropanol (IPA, •OH scavenger) (Cao et al., 2012), ammonium oxalate (AO, h+ scavenger) (Chang et al., 2013) and p-benzoquinone (BQ, •O2-scavenger) (Sun et al., 2017) have been added separately in the degradation systems. When BQ and AO were introduced, the degradation rate of OFX decreased significantly (see Figure 9). Moreover, the degradation rate of OFX was also decreased in the presence of IPA. These results indicate that h+ and •O2- play an important role in the degradation process. •OH has a certain effect on the degradation of OFX. Therefore, we can conclude that the free radicals of •O2-, h+ and •OH in active species play a certain role in the degradation of OFX.

Figure 9.

Figure 9

Open in a new tab

Trapping experiment of active species during the photocatalytic degradation of OFX over BN-3 under UV light irradiation.

The formation of heterojunction in the composite system has a positive effect on the separation of photogenerated electrons and holes. Based on the above experimental results, we propose a reasonable photocatalytic mechanism for BiOCl/NaNbO3 (Scheme 1). The enhanced photocatalytic activity of BiOCl/NaNbO3 heterojunction originates from the unique matching band location of these two semiconductors after forming heterojunction. Based on the experimental data, we know that the band gap of BiOCl is larger than that of NaNbO3. The Fermi level (Ef) of BiOCl is located near the valence band because it is a p type semiconductor, and the Fermi level of n type semiconductor NaNbO3 approaches the conduction band. When the mixture of BiOCl and NaNbO3 forms a p-n type heterojunction of BiOCl/NaNbO3, the Fermi level of BiOCl moves upwards, while the Fermi level of the NaNbO3 moves downward until the Fermi level of BiOCl and NaNbO3 is at the same level. Finally, the CB position of BiOCl becomes higher than NaNbO3 after moving up. At the same time, BiOCl and NaNbO3 form an internal electric field in the final equilibrium state. At the same time, the valence band (VB) of NaNbO3 is also lower than that of BiOCl. Due to the special band structure of the BiOCl/NaNbO3 composite, the photoelectrons are excited from the VB of the BiOCl to the CB, because the special ladder like structure of the BiOCl/NaNbO3 heterostructure leads to the electronic transfer from CB of BiOCl to the CB of NaNbO3. Electrons stored in NaNbO3's CB can react with dissolved O2 to form •O2-, while the adsorbed hydroxy or H2O molucules can also react with h+ to form •OH or directly oxidize organic pollutants. Therefore, the formed p-n junction between BiOCl and NaNbO3 provide an effective electron transfer path to reduce the recombination of electron-hole pairs, thus improving the activity of the as fabricated BiOCl/NaNbO3 composites.

Scheme 1.

Scheme 1

Open in a new tab

Proposed possible mechanism of the photocatalytic degradation of pollutants over BiOCl/NaNbO3 p–n junction under UV light irradiation.

Conclusions

In this work, BiOCl/NaNbO3 composites with p-n heterojunctions were synthesized by simple hydrothermal method. Through experiments and characterization, it is confirmed that p-n junctions formed on the interface between BiOCl and NaNbO3. The results indicted that the separation efficiency of photo-generated carriers has been greatly improved because of the formation of p-n junctions. Recycle experiments showed that the composite photocatalyst exhibited good stability. The experimental results also show that pollutants are mainly degraded by h+ and ·O2- radicals. Therefore, BiOCl/NaNbO3 heterojunction nanocomposites can be used as a highly efficient and reusable photocatalyst, which has potential applications in the removal of organic pollutants.

Author contributions

JX and MC designed the project, guided the study and polished the manuscript. BF, YW, and YQ conducted the experiments and characterized the samples. JN revised the manuscript.

Conflict of interest statement

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

Acknowledgments

We are grateful for grants from the Priority Academic Program Development of Jiangsu Higher Education Institutions (PAPD).

References

  1. Ao Y. H., Bao J. Q., Wang P. F., Wang C., Hou J. (2016a). Bismuth oxychloride modified titanium phosphate nanoplates: a new p-n type heterostructured photocatalyst with high activity for the degradation of different kinds of organic pollutants. J. Colloid Interface Sci. 476, 71–78. 10.1016/j.jcis.2016.05.021 [DOI] [PubMed] [Google Scholar]
  2. Ao Y. H., Wang K. D., Wang P. F., Wang C., Hou J. (2016b). Synthesis of novel 2D-2D p-n heterojunction BiOBr/La2Ti2O7 composite photocatalyst with enhanced photocatalytic performance under both UV and visible light irradiation. Appl. Catal. B Environ. 194, 157–168. 10.1016/j.apcatb.2016.04.050 [DOI] [Google Scholar]
  3. Cao J., Xu B. Y., Lin H. L., Luo B. D., Chen S. F. (2012). Novel Bi2S3-sensitized BiOCl with highly visible light photocatalytic activity for the removal of rhodamine B. Catal. Commun. 26, 204–208. 10.1016/j.catcom.2012.05.025 [DOI] [Google Scholar]
  4. Cao M., Wang P., Ao Y., Wang C., Hou J., Qian J. (2016). Visible light activated photocatalytic degradation of tetracycline by a magnetically separable composite photocatalyst: graphene oxide/magnetite/cerium-doped titania. J. Colloid Interface Sci. 467, 129–139. 10.1016/j.jcis.2016.01.005 [DOI] [PubMed] [Google Scholar]
  5. Chang C., Zhu L. Y., Fu Y., Chu X. L. (2013). Highly active Bi/BiOI composite synthesized by one-step reaction and its capacity to degrade bisphenol A under simulated solar light irradiation. Chem. Eng. J. 233, 305–314. 10.1016/j.cej.2013.08.048 [DOI] [Google Scholar]
  6. Chen P., Dong F., Ran M. X., Li J. R. (2018). Synergistic photo-thermal catalytic NO purification of MnOx/g-C3N4: enhanced performance and reaction mechanism. Chin. J. Catal. 39, 619–629. 10.1016/S1872-2067(18)63029-3 [DOI] [Google Scholar]
  7. Chen S. F., Hu Y. F., Ji L., Jiang X. L., Fu X. L. (2014). Preparation and characterization of direct Z-scheme photocatalyst Bi2O3/NaNbO3 and its reaction mechanism. Appl. Surf. Sci. 292, 357–366. 10.1016/j.apsusc.2013.11.144 [DOI] [Google Scholar]
  8. Fan M. S., Hu B., Yan X., Song C. J., Chen T. J., Feng Y., et al. (2015). Excellent visible-light-driven photocatalytic performance of Cu2O sensitized NaNbO3 heterostructures. New J. Chem. 39, 6171–6177. 10.1039/C5NJ00751H [DOI] [Google Scholar]
  9. Fang S. S., Ding C. Y., Liang Q., Li Z. Y., Xu S., Peng Y. Y., et al. (2016). In-situ precipitation synthesis of novel BiOCl/Ag2CO3 hybrids with highly e?cient visible-light-driven photocatalytic activity. J. Alloy. Compd. 684, 230–236. 10.1016/j.jallcom.2016.05.168 [DOI] [Google Scholar]
  10. Guo Y., Wang P. F., Qian J., Ao Y. H., Wang C., Hou J. (2018). Phosphate group grafted twinned BiPO4 with significantly enhanced photocatalytic activity: synergistic effect of improved charge separation efficiency and redox ability. Appl. Catal. B Environ. 234, 90–99. 10.1016/j.apcatb.2018.04.036 [DOI] [Google Scholar]
  11. Han W., Liu Z., Li Y., Fan X., Zhang F., Zhang G., et al. (2018). The promoting role of different carbon allotropes cocatalysts for semiconductors in photocatalytic energy generation and pollutants degradation. Front. Chem. 5:84. 10.3389/fchem.2017.00084 [DOI] [PMC free article] [PubMed] [Google Scholar]
  12. He S., Hou P., Petropoulos E., Feng Y., Yu Y., Xue L., et al. (2018). High efficient visible-light photocatalytic performance of Cu/ZnO/rGO nanocomposite for decomposing of aqueous ammonia and treatment of domestic wastewater. Front. Chem. 6:219. 10.3389/fchem.2018.00219 [DOI] [PMC free article] [PubMed] [Google Scholar]
  13. Hu J. L., Wu X. X., Huang C. J., Fan W. J., Qiu X. Q. (2016). Visible light photocatalytic activity induced by Rh(III) modification on the surface of BiOCl. Appl. Surf. Sci.387, 45–50. 10.1016/j.apsusc.2016.06.075 [DOI] [Google Scholar]
  14. Katsumata K., Okazaki S., Cordonier C. E., Shichi T., Sasaki T., Fujishima A. (2010). Preparation and characterization of self-cleaning glass for vehicle with niobia nanosheets. ACS Appl. Mater. Interfaces 2, 1236–1241. 10.1021/am100091f [DOI] [PubMed] [Google Scholar]
  15. Kuang P. Y., Su Y. Z., Chen G. F., Luo Z., Xing S. Y., Li N., et al. (2015). g-C3N4 decorated ZnO nanorod arrays for enhanced photoelectrocatalytic performance. Appl. Surf. Sci. 358, 296–303. 10.1016/j.apsusc.2015.08.066 [DOI] [Google Scholar]
  16. Kumar S., Khanchandani S., Thirumal M., Ganguli A. K. (2014). Achieving enhanced visible-light-driven photocatalysis using type-II NaNbO3/CdS core/shell heterostructures. ACS Appl. Mater. Interfaces 6, 13221–13233. 10.1021/am503055n [DOI] [PubMed] [Google Scholar]
  17. Li G., Kako T., Wang D., Zou Z., Ye J. (2008). Synthesis and enhanced photocatalytic activity of NaNbO3 prepared by hydrothermal and polymerized complex methods. J. Phys. Chem. Solids 69, 2487–2491. 10.1016/j.jpcs.2008.05.001 [DOI] [Google Scholar]
  18. Li G., Yi Z., Bai Y., Zhang W., Zhang H. (2012a). Anisotropy in photocatalytic oxidization activity of NaNbO3 photocatalyst. Dalton Trans. 41, 10194–10198. 10.1039/c2dt30593c [DOI] [PubMed] [Google Scholar]
  19. Li G. Q. (2010). Photocatalytic properties of NaNbO3 and Na0.6Ag0.4NbO3 synthesized by polymerized complex method. Mater. Chem. Phys. 121, 42–46. 10.1016/j.matchemphys.2009.12.032 [DOI] [Google Scholar]
  20. Li P., Ouyang S., Xi G., Kako T., Ye J. H. (2012b). The effects of crystal structure and electronic structure on photocatalytic H2 evolution and CO2 reduction over two phases of perovskite-structured NaNbO3. J. Phys. Chem. C 116, 7621–7628. 10.1021/jp210106b [DOI] [Google Scholar]
  21. Li P., Ouyang S. X., Zhang Y. J., Kako T., Ye J. H. (2013). Surface-coordination-induced selective synthesis of cubic and orthorhombic NaNbO3 and their photocatalytic properties. J. Mater. Chem. A 1, 1185–1191. 10.1039/C2TA00260D [DOI] [Google Scholar]
  22. Li P., Xu H., Liu L. Q., Kako T., Umezawa N., Abe H., et al. (2014). Constructing cubic–orthorhombic surface-phase junctions of NaNbO3 towards significant enhancement of CO2 photoreduction. J. Mater. Chem. A 2, 5606–5609. 10.1039/C4TA00105B [DOI] [Google Scholar]
  23. Li Q., Li X., Wageh S., Al-Ghamdi A. A., Yu J. (2015). CdS/Graphene nanocomposite photocatalysts. Adv. Energy Mater. 5:1500010 10.1002/aenm.201500010 [DOI] [Google Scholar]
  24. Li S., Hu S., Jiang W., Liu Y., Liu Y., Zhou Y. T., et al. (2018). Ag3VO4 nanoparticles decorated Bi2O2CO3 micro-flowers: an efficient visible-light-driven photocatalyst for the removal of toxic contaminants. Front. Chem. 6:255. 10.3389/fchem.2018.00255 [DOI] [PMC free article] [PubMed] [Google Scholar]
  25. Liu M. R., Hong Q. L., Li Q. H., Du Y. H., Zhang H. X., Chen S. M., et al. (2018). Cobalt boron imidazolate framework derived cobalt nanoparticles encapsulated in B/N codoped nanocarbon as efficient bifunctional electrocatalysts for overall water splitting. Adv. Funct. Mater. 28:1801136 10.1002/adfm.201801136 [DOI] [Google Scholar]
  26. Liu Q. Q., Chai Y. Y., Zhang L., Ren J., Dai W. L. (2016). Highly efficient Pt/NaNbO3 nanowire photocatalyst: Its morphology effect and application in water purification and H2 production. Appl. Catal. B Environ. 205, 505–513. 10.1016/j.apcatb.2016.12.065 [DOI] [Google Scholar]
  27. Liu W. W., Qiao L. L., Zhu A. Q., Liu Y., Pan J. (2017a). Constructing 2D BiOCl/C3N4 layered composite with large contact surface for visible-light-driven photocatalytic degradation. Appl. Surf. Sci. 426, 897–905. 10.1016/j.apsusc.2017.07.225 [DOI] [Google Scholar]
  28. Liu W. W., Shang Y. Y., Zhu A. Q., Tan P. F., Liu Y., Qiao L. L., et al. (2017b). Enhanced performance of doped BiOCl nanoplates for photocatalysis: understanding from doping insight into improved spatial carrier separation. J. Mater. Chem. A 5:12542–12549. 10.1039/C7TA02724A [DOI] [Google Scholar]
  29. Lv J., Kako T., Li Z. S., Zou Z. G., Ye J. H. (2010). Synthesis and photocatalytic activities of NaNbO3 rods modified by In2O3 nanoparticles. J. Phys. Chem. C 114, 6157–6162. 10.1021/jp906550t [DOI] [Google Scholar]
  30. Ma W., Chen L., Zhu Y. Z., Dai J. D., Yan Y. S., Li C. X. (2016). Facile synthesis of the magnetic BiOCl/ZnFe2O4 heterostructures with enhanced photocatalytic activity under visible-light irradiation. Colloids Surfaces A Physicochem Eng. Aspects. 508, 135–141. 10.1016/j.colsurfa.2016.08.066 [DOI] [Google Scholar]
  31. Ma Y. C., Chen Z. W., Qu D., Shi J. S. (2016). Synthesis of chemically bonded BiOCl@Bi2WO6 microspheres with exposed (020) Bi2WO6 facets and their enhanced photocatalytic activities under visible light irradiation. Appl. Surf. Sci. 361, 63–71. 10.1016/j.apsusc.2015.11.130 [DOI] [Google Scholar]
  32. Mao D. J., Yu A. Q., Ding S. S., Wang F., Yang S. G., Sun C., et al. (2016). One-pot synthesis of BiOCl half-shells using microemulsion droplets astemplates with highly photocatalytic performance for the degradation of ciprofloxacin. Appl. Surf. Sci. 389, 742–750. 10.1016/j.apsusc.2016.07.178 [DOI] [Google Scholar]
  33. Qian J., Xue Y., Ao Y. H., Wang P. F., Wang C. (2018). Hydrothermal synthesis of CeO2/NaNbO3 composites with enhanced photocatalytic performance. Chin. J. Catal. 39, 682–692. 10.1016/S1872-2067(17)62975-9 [DOI] [Google Scholar]
  34. Rajeshwar K., de Tacconi N. R., Chenthamarakshan C. R. (2001). Semiconductor-based composite materials: preparation, properties, and performance. Chem. Mater. 13, 2765–2782. 10.1021/cm010254z [DOI] [Google Scholar]
  35. Saito K., Kudo A. (2013). Fabrication of highly crystalline SnNb2O6 shell with a visible-light response on a NaNbO3 nanowire core. Inorg. Chem. 52, 5621–5623. 10.1021/ic4002175 [DOI] [PubMed] [Google Scholar]
  36. Shang M., Wang W. Z., Zhang L., Zhou L. (2009). 3D Bi2WO6/TiO2 hierarchical heterostructure: controllable synthesis and enhanced visible photocatalytic degradation performances. J. Phys. Chem. C 113, 14727–14731. 10.1021/jp9045808 [DOI] [Google Scholar]
  37. Shi H. F., Chen G. Q., Zhang C. L., Zou Z. G. (2014b). Polymeric g-C3N4 coupled with NaNbO3 nanowires toward enhanced photocatalytic reduction of CO2 into renewable fuel. ACS Catal. 4, 3637–3643. 10.1021/cs500848f [DOI] [Google Scholar]
  38. Shi H. F., Chen G. Q., Zou Z. G. (2014a). Platinum loaded NaNbO3-xNx with nanostep surface nanostructures toward enhanced visible-light photocatalytic activity. Appl. Catal. B Environ. 156, 378–384. 10.1016/j.apcatb.2014.03.036 [DOI] [Google Scholar]
  39. Shifu C., Ji L., Tang W. M., Fu X. L. (2013). Fabrication, characterization and mechanism of a novel Z-scheme photocatalyst NaNbO3/WO3 with enhanced photocatalytic activity. Dalton Trans. 42, 10759–10768. 10.1039/c3dt50699a [DOI] [PubMed] [Google Scholar]
  40. Song C. J., Fan M. S., Hu B., Chen T. J., Wang L. P., Shi W. D. (2015). Synthesis of a g-C3N4-sensitized and NaNbO3-substrated II-type heterojunction with enhanced photocatalytic degradation activity. Cryst. Eng. Comm. 17, 4575–4583. 10.1039/C5CE00622H [DOI] [Google Scholar]
  41. Sun M., Yan Q., Shao Y., Wang C. Q., Yan T., Ji P. G., et al. (2017). Facile fabrication of BiOI decorated NaNbO3 cubes: a p–n junction photocatalyst with improved visible-light activity. Appl. Surf. Sci. 416, 288–295. 10.1016/j.apsusc.2017.04.136 [DOI] [Google Scholar]
  42. Wang D. H., Gao G. Q., Zhang Y. W., Zhou L. S., Xu A. W., Chen W. (2012). Nanosheet-constructed porous BiOCl with dominant {001} facets for superior photosensitized degradation. Nanoscale 4, 7780–7785. 10.1039/c2nr32533k [DOI] [PubMed] [Google Scholar]
  43. Wang H., Zhang W. D., Li X. W., Li J. Y., Cen W. L., Li Q. Y., et al. (2018). Highly enhanced visible light photocatalysis and in situ FT-IR studies on Bi metal@defective BiOCl hierarchical microspheres. Appl. Catal. B Environ. 225, 218–227. 10.1016/j.apcatb.2017.11.079 [DOI] [Google Scholar]
  44. Xu Y., Mo Y. P., Tian J., Wang P., Yu H. G., Yu J. G. (2016). The synergistic effect of graphitic N and pyrrolic N for the enhanced photocatalytic performance of nitrogen-doped graphene/TiO2 nanocomposites. Appl. Catal. B Environ. 181, 810–817. 10.1016/j.apcatb.2015.08.049 [DOI] [Google Scholar]
  45. Yan M., Hua Y. Q., Zhu F. F., Gu W., Jiang J. H., Shen H. Q., et al. (2017). Fabrication of nitrogen doped graphene quantum dots-BiOI/MnNb2O6 p–n junction photocatalysts with enhanced visible light efficiency in photocatalytic degradation of antibiotics. Appl. Catal. B Environ. 202, 518–527. 10.1016/j.apcatb.2016.09.039 [DOI] [Google Scholar]
  46. Yang Y., Zhang Q., Zhang R. Y., Ran T., Wan W. C., Zhou Y. (2018). Compressible and recyclable monolithic g-C3N4/melamine sponge: a facile ultrasonic-coating approach and enhanced visible-light photocatalytic activity. Front. Chem. 6:156. 10.3389/fchem.2018.00156 [DOI] [PMC free article] [PubMed] [Google Scholar]
  47. Ye L. Q., Su Y. R., Jin X. L., Xie H., Zhang C. (2014). Recent advances in BiOX (X = Cl, Br and I) photocatalysts: synthesis modification, facet effects and mechanisms. Environ. Sci. Nano. 1, 90–112. 10.1039/c3en00098b [DOI] [Google Scholar]
  48. Yu H. G., Xiao P., Tian J., Wang F. Z., Yu J. G. (2016). Phenylamine-functionalized rGO/TiO2 photocatalysts: spatially separated adsorption sites and tunable photocatalytic selectivity. ACS Appl. Mat. Interfaces 8, 29470–29477. 10.1021/acsami.6b09903 [DOI] [PubMed] [Google Scholar]
  49. Yuan X. Z., Wang H., Wang J. J., Zeng G. M., Chen X. H., Wu Z. B., et al. (2018). Near-infrared-driven Cr (VI) reduction in aqueous solution based on a MoS2/Sb2S3 photocatalyst. Catal. Sci. Technol. 8, 1545–1554. 10.1039/C7CY02531A [DOI] [Google Scholar]
  50. Zhang B. B., Zhang D. F., Xi Z. S., Wang P. F., Pu X. P., Shao X., et al. (2017). Synthesis of Ag2O/NaNbO3 p-n junction photocatalysts with improved visible light photocatalytic activities. Sep. Purification Technol. 178, 130–137. 10.1016/j.seppur.2017.01.031 [DOI] [Google Scholar]
  51. Zhang J. F., Wageh S., Al-Ghamdic A., Yu J. G. (2016). New understanding on the different photocatalytic activity of wurtzite and zinc-blende CdS. Appl. Catal. B Environ. 192, 101–107. 10.1016/j.apcatb.2016.03.058 [DOI] [Google Scholar]
  52. Zhang J. Y., Xiao F. X. (2017). Modulation of interfacial charge transfer by self-assembly of single-layer graphene enwrapped one-dimensional semiconductors toward photo redox catalysis. J. Mat. Chem. A. 5, 23681–23693. 10.1039/C7TA08415C [DOI] [Google Scholar]
  53. Zhang W. D., Liu X. L., Dong X. A., Dong F., Zhang Y. X. (2017a). Facile synthesis of Bi12O17Br2 and Bi4O5Br2 nanosheets: in situ DRIFTS investigation of photocatalytic NO oxidation conversion pathway. Chin. J. Catal. 38, 2030–2038. 10.1016/S1872-2067(17)62941-3 [DOI] [Google Scholar]
  54. Zhang W. D., Zhao Z. W., Dong F., Zhang Y. X. (2017b). Solvent-assisted synthesis of porous g-C3N4 with efficient visible-light photocatalytic performance for NO removal. Chin. J. Catal. 38, 372–378. 10.1016/S1872-2067(16)62585-8 [DOI] [Google Scholar]
  55. Zhong Y. X., Liu Y. H., Wu S., Zhu Y., Chen H. B., Yu X. (2018). Facile fabrication of BiOI/BiOCl immobilized films with improved visible light photocatalytic performance. Front. Chem. 6:58. 10.3389/fchem.2018.00058 [DOI] [PMC free article] [PubMed] [Google Scholar]
  56. Zhou T. H., Du Y. H., Wang D. P., Yin S. M., Tu W. G., Chen Z., et al. (2017). Phosphonate-based metal-organic framework derived Co-P-C hybrid as an efficient electrocatalyst for oxygen evolution reaction. ACS Catal. 7:6000–6007. 10.1021/acscatal.7b00937 [DOI] [Google Scholar]

Articles from Frontiers in Chemistry are provided here courtesy of Frontiers Media SA

RESOURCES