Introduction
Considering environmental problems and the exhausting supply of global energy, it is urgently necessary to exploit sustainable energy systems. Solar energy, as a clean, renewable, and abundant energy, is one of the most promising candidates to substitute for fossil fuels. With a specific energy density of 120 kJ·g
−1 and only water (H
2O) as a byproduct when consumed, hydrogen (H
2) is considered to be an efficient energy carrier as well as the cleanest option [
1–
3]. Moreover, H
2 can be stored and carried over a long distance as a stable energy supply [
2–
4]. Photocatalytic water splitting, which stores solar energy in H—H (H
2) bonds, is a simple and green solar-energy-conversion approach [
1], and has therefore attracted global research interest during the past decades. Many materials have been investigated for solar water splitting with the hope of achieving a commercially feasible solar-to-hydrogen (STH) efficiency of over 10% [
5–
10]. To date, some material systems can achieve overall water splitting, but most of these photocatalysts can only be active under ultraviolet (UV) light irradiation (which accounts for only 4% of solar energy) [
11–
14]. Only limited material systems, such as In
1–xNi
xTaO
4 (
x = 0–0.2) [
15], (Ga
1–xZn
x)(N
1–xO
x) [
16], (Zn
1+xGe)(N
2O
x) [
17], TaON [
18], C
3N
4 [
19,
20], and LaMg
xTa
1–xO
1+3xN
2–3x (
x = 0–2/3) [
21], are able to achieve visible-light-responsible water splitting. However, the STH efficiency of these photocatalysts is still too low for practical application. Many metal dichalcogenides (e.g., CdS, CdSe, and CuInS
2), which can absorb visible light, show highly efficient photocatalytic H
2 evolution from water with sacrificial agents [
22–
24]. However, most suffer from photocorrosion, which damages the long-term stability of these photocatalysts. Therefore, the question of how to better design and develop low-cost and stable photocatalysts for efficient water splitting is of great importance.
As many excellent reviews for photocatalytic water splitting have been published [
6,
7,
11,
12,
25–
35], we provide only a brief introduction to the photocatalytic water-splitting mechanism here. As shown in Fig. 1, the major steps in a photocatalytic water-splitting reaction are as follows.
(1) Photon absorption and electron-hole pair generation. During this process, only photons with energy higher than the bandgap energy of the semiconductor are effective for excitation. Once excited, electrons from valence bands (VBs) jump to conduction bands (CBs), and holes are left in the VBs. The photo-excited electrons and holes lead to redox reactions on H2O, electrons for water reduction, and holes for water oxidation. As illustrated in Fig. 2, the energy potential of the CB minimum and VB maximum are key points for the photocatalytic reaction. The CB minimum should be more negative than the H2 production potential (0 V vs. normal hydrogen electrode (NHE)) while the VB maximum should be more positive than the oxygen production potential (1.23 V). Otherwise, the photocatalysts can only conduct a half reaction with the assistance of sacrificial agents, which will increase the cost of the hydrogen produced.
(2) Separation and transfer of electrons. Photo-generated electron-hole pairs separate and migrate to the surface to take part in the water redox reaction. During this process, charge carriers easily meet each other and recombination occurs, which is undesirable for photocatalysis.
(3) Surface chemical reactions. In this step, the photo-excited charge carriers on the surface active sites react with water.
Due to the 10% STH conversion efficiency that is required for commercial application, the development of highly efficient photocatalysts that can maximize the efficiency of each of the three steps mentioned above is extremely important [
1,
36–
38]. The theoretical maximum STH efficiency depends on the bandgap of the photocatalysts, because only light with energy higher than the bandgap of the photocatalysts can be absorbed and used for the water redox reaction. Theoretically, the bandgap should be a minimum of 1.23 eV. However, due to the thermodynamic energy (~ 0.4 eV) and kinetic loss (~ 0.4 eV), a bandgap of 2 eV is usually necessary for overall photocatalytic water splitting [
11]. For photocatalysts with a bandgap energy ranging from 2.0 eV to 2.5 eV, the theoretical STH efficiency ranges from 10% to 16% under simulated sunlight irradiation (air mass 1.5 global, AM 1.5G) [
39]. Considering the energy loss in practical applications, a narrow bandgap is a key criterion for photocatalysts to achieve high STH efficiency. Here, we define narrow bandgap photocatalysts as photocatalysts with a bandgap no greater than 2.5 eV (corresponding to ~500 nm light absorption).
Tantalum (oxy)nitride-based photocatalysts, which have bandgaps varying from 1.9 eV to 2.5 eV and bandgap positions that are suitable for water splitting, are considered to be a group of potential photocatalysts for efficient water splitting [
39]. Over the past years, great development and encouraging progress have been achieved in tantalum (oxy)nitride-based photocatalysts. However, the STH efficiency of these photocatalysts is still less than 1% [
40–
45]. One major problem is the asymmetric capability of these materials for water reduction and oxidation. Tantalum (oxy)nitride-based photocatalysts have shown a comparably much higher water oxidation capability than water reduction capability [
40,
46–
48]. Because overall water splitting is a synergistic reaction system between water reduction and water oxidation, a relatively weaker water reduction capability will inevitably impede the overall water-splitting reaction. Thus, it is of great importance to improve the water reduction efficiency of tantalum (oxy)nitride-based photocatalysts. In addition, both surface defects and self-oxidation damage the long-term stability of tantalum (oxy)nitride-based photocatalysts. This review provides an up-to-date critical review on narrow bandgap tantalum (oxy)nitride-based photocatalysts for water splitting. In particular, recent progress in the development of effective strategies for enhancing their water reduction capability is discussed. An outlook perspective for further development of tantalum (oxy)nitride-based photocatalysts is also proposed.
Tantalum-based narrow bandgap photocatalysts
Tantalum (oxy)nitride-based photocatalysts are a large family; the main research focus is on Ta
3N
5, TaON, LaTaON
2, and ATaO
2N (A= Ca, Sr, Ba), which possess narrow bandgaps and suitable band positions for the water redox reaction [
49]. Among these, Ta
3N
5 and TaON have been intensely studied, and over 10% quantum efficiency (QE) for water oxidation and 9.5% QE for water reduction have been achieved [
43,
47,
48]. In addition, BaTaO
2N has shown H
2 evolution from water without sacrificial agents by forming a solid solution with BaZrO
3, and TaON was demonstrated to show overall water-splitting activity with surface modification and appropriate co-catalysts [
18,
50]. Moreover, very recent progress showed that LaMg
xTa
1–xO
1+3xN
2–3x and CaTaO
2N could achieve overall water splitting when a Rh-Cr bimetallic oxide co-catalyst was loaded on the surface [
51]. All these findings strongly indicate the great potential of tantalum (oxy)nitride-based narrow bandgap photocatalysts for achieving highly efficient solar water splitting.
Basic properties of tantalum (oxy)nitrides
Many reviews have introduced and discussed the fundamental parameters, optical properties, and electronic properties of tantalum (oxy)nitride-based materials, both theoretically and experimentally [
14,
30,
41,
42,
52,
53]. Here, we briefly introduce the basic properties that are relevant to photocatalytic performance. Table 1 [
49] presents typical tantalum (oxy)nitride-based photocatalysts. Ta
3N
5 and TaON show anosovite- and baddelyite-type crystal structures, respectively, while the others are perovskite-type crystals. The bandgap ranges from 1.9 eV to 2.4 eV, and corresponds to as long as 660 nm light absorption. The absolute position of the CB minimum and of the VB maximum is one of the key factors that influences the water reduction and water oxidation capability of photocatalysts. Domen et al. [
54] experimentally identified the CB and VB positions of Ta
3N
5 and TaON by combining UV photoelectron spectroscopy (UPS) with electrochemical analysis. As shown in Fig. 3 [
54], the CB minimums of Ta
3N
5 and TaON are ~−0.3 eV and ~−0.5 eV, respectively, versus NHE at pH= 0, while the VB maximums of Ta
3N
5 and TaON are ~1.6 eV and ~2.1 eV, respectively. The bandgap positions indicate that both Ta
3N
5 and TaON can be used for the photocatalytic water redox reaction. Balaz et al. [
55] investigated the bandgap positions of tantalum oxynitride perovskite (ATaO
2N, A= Ca, Sr, Ba) by combining depth-resolve cathodoluminescence spectroscopy (DRCLS), ultraviolet-visible (UV-Vis) spectroscopy, Kelvin probe force microscopy (KPFM), and X-ray photoemission spectroscopy (XPS). As shown in Fig. 4 [
55], all of the VB maximums except that of PrTaO
2N are more positive than the oxygen evolution potential of water, and the CB minimums are more negative than the hydrogen evolution potential. Based on the investigation of band structure and the study of photocatalytic water-splitting activity, it is anticipated that tantalum (oxy)nitride-based materials can be designed as highly efficient catalysts for solar water splitting.
Synthesis of tantalum (oxy)nitrides
In general, tantalum (oxy)nitride-based materials are synthesized from tantalum-based oxide precursors via nitridation at high temperature with ammonia (NH
3) gas as the nitrogen source [
14]. For Ta
3N
5 and TaON, many preparation methods have been reported to synthesize Ta
2O
5 precursors, including reverse homogeneous precipitation reactive sputtering, atomic layer deposition, and vapor phase hydrothermal processes [
56–
61]. For the tantalum-based oxynitride perovskite, a solid-state reaction is normally applied to synthesize the oxide precursors. The key step to transform the precursors into (oxy)nitride is high-temperature thermal treatment in NH
3 gas. The nitridation conditions, such as temperature, pressure, and precursor, are important to the final photocatalytic performance [
62–
64].
The nitridation temperature, duration, and NH
3 gas flow determine the final products. During the nitridation process, the oxygen (O) atoms are substituted by nitrogen (N) atoms. When using Ta
2O
5 as the precursor, low temperature, short time, and low NH
3 gas flow lead to a slow reaction and to the partial substitution of O atoms by N atoms, resulting in TaON as the final product. To obtain oxygen-free Ta
3N
5, higher temperature (>850 °C), longer treatment (>10 h), and higher NH
3 gas flow (>20 mL·min
−1) are necessary. The influence of nitridation temperature on the photocatalytic performance of Ta
3N
5 has been systematically studied [
62]. During the nitridation process, the duration and NH
3 gas flow were fixed, with the only variation being that of temperature. Once the temperature was above 850 °C, Ta
3N
5 could be obtained. Further increasing the temperature to 950 °C did not influence the structural and optical properties of Ta
3N
5. However, increasing the temperature to 1000 °C led to the formation of a tantalum (Ta) reduced species, which was confirmed by the sub-bandgap absorption that was observed in the UV-Vis light absorption spectrum (Fig. 5) [
62]. The Ta reduced species acted as a recombination center, and samples with such defects showed lower photocatalytic performance. Thus, suitable nitridation temperature is important to obtain Ta
3N
5 with good crystallinity and pure phase.
Pressure is another factor that influences the final performance of tantalum (oxy)nitride photocatalysts [
65]. Kishida and Watanabe [
64] studied the effect of pressure on the final photocatalytic H
2 generation reaction of Ta
3N
5. It was demonstrated that Ta
3N
5 obtained under high-pressure ammonothermal treatment (>50 MPa) showed improved photocatalytic H
2 evolution efficiency. The improved performance was attributed to the decrease of surface defects, which reduced surface recombination and improved the transfer of electrons to the surface active sites (platinum (Pt) co-catalyst or surface H
+). A higher density of defects was expected to cause stronger absorption at a wavelength longer than the absorption edge of the semiconductors [
46,
66–
68]. Ta
3N
5 treated with an ammonia pressure of 50 MPa showed the lowest absorption intensity and the highest photocatalytic activity (Fig. 6) [
64]. Thus, high-pressure ammonothermal treatment should be an effective way to suppress surface defects and enhance the photocatalytic activity of tantalum (oxy)nitride-based photocatalysts.
In addition to pressure, flux-assisted nitridation was adopted to synthesize the Ta
3N
5 photocatalysts with high crystallinity. Takata et al. [
69] conducted a systematic study of flux-assisted nitridation for Ta
3N
5 preparation. Zinc (Zn), NaCl, and Na
2CO
3 were used as flux during the nitridation of Ta
2O
5 or TaCl
5 into Ta
3N
5. It was found that the introduction of NaCl and Na
2CO
3 as flux during the nitridation process led to the formation of morphologically defined particles. When TaCl
5 was nitrided along with NaCl, well-crystallized Ta
3N
5 nanoparticles were obtained (Fig. 7) [
69]. In addition, the particle size could be controlled by varying the temperature. It was explained that nitridation and dissolution might happen simultaneously during flux-assisted nitridation, which would more effectively promote the diffusion of atoms in the materials. This result demonstrates that the morphology, dispersity, crystallinity, and surface states of tantalum (oxy)nitride can be controlled by varying the nitridation conditions, including temperature, ammonia pressure, precursor, and flux.
Strategies for improving water-splitting activity
The three main steps in photocatalytic water splitting, namely, light absorption, charge carrier migration, and surface redox reaction, have a synergistic effect on the activity of photocatalytic water splitting. Based on these three steps, many strategies including doping, morphological control, surface modification, co-catalyst design, and heterostructure design have been intensively explored in order to enhance the water-splitting activity of tantalum (oxy)nitride-based photocatalysts.
Doping
Heteroatom doping is an important strategy to tune the basic properties of photocatalysts, such as bandgap structures, electronic conductivity, and surface structure. Doping is usually used to narrow the bandgap, increase the electronic conductivity, or make the surface active, thus promoting light harvesting, charge transfer reactions, and surface reactions. Through doping, the water-splitting performance of photocatalysts is significantly improved [
70–
75]. Foreign-ion-doped tantalum (oxy)nitride photoanodes or photocatalysts for O
2 evolution have been prepared and investigated intensively [
76–
80], but limited research attention has been paid to the H
2 evolution of doped tantalum (oxy)nitride-based photocatalysts. Seo et al. [
81] systematically investigated magnesium (Mg)- and zirconium (Zr)-doped Ta
3N
5 photocatalysts for H
2 evolution. As shown in Fig. 8(a) [
81], single substitution with Mg or Zr enhanced H
2 evolution by several times, while the activity of Ta
3N
5:Mg+ Zr (doping concentration: 25 at%) for H
2 evolution was increased drastically, to approximately 15 times the performance of pure Ta
3N
5. According to the band structure investigation, the enhanced H
2 evolution activity was attributed to the negative shift of bandgap (Fig. 8(b)) [
81]. The Mg+ Zr co-doped Ta
3N
5 had a more negative CB and thus possessed a higher reduction potential, which favored water reduction.
When Mg ions were introduced into LaTaON
2, the resulting solid solution of LaMg
xTa
1–xO
1+3xN
2–3x (
x = 0–2/3) acted as a photocatalyst for water splitting at light absorptions up to 600 nm [
21]. Further investigation revealed that the introduction of Mg ions enabled fine-tuning of the bandgap energy and positions, resulting from a co-substitution of Mg
2+ for Ta
5+ and O
2– for N
3–. As shown in Fig. 9(a) [
82], the bandgap energy of LaMg
xTa
1–xO
1+3xN
2–3x could easily be tuned by varying the Mg/(Mg+ Ta) ratio. The absolute bandgap position of LaMg
0.33Ta
0.67O
2N was revealed by combining photoelectron spectroscopy in air (PESA) with theoretical calculations. Both methods confirmed the negative shift of the CB and positive shift of the VB for LaMg
0.33Ta
0.67O
2N compared with LaTaON
2 (Fig. 9(b)) [
82]. An increased redox potential can enhance the water reduction and oxidation capability of photocatalysts, resulting in overall water splitting.
Morphological control
The morphology and particle size of the photocatalysts play important roles in charge separation and migration, as well as in surface reactions [
12,
83]. Smaller particle size means a shorter migration distance and a higher specific surface area. More photo-generated charge carriers can move to the surface and take part in the water redox reaction. Ta
3N
5 and TaON are typically obtained by the nitridation of Ta
2O
5 precursor. Various methods have been adopted to reduce the size of particles and control the morphology of the Ta
2O
5 precursor. However, phase transition occurs during high-temperature nitridation, which may cause the breakdown of nanostructures. Hisatomi et al. [
84] solved this problem by coating the surface of the mesoporous Ta
2O
5 precursor with a silica layer before nitridation. The silica layer, which was obtained by chemical vapor deposition of tetramethyl orthosilicate, was used to support the mesoporous structure of Ta
2O
5 during high-temperature nitridation. As shown in Fig. 10(a) [
84], ordered mesoporous Ta
3N
5 was obtained. The photocatalytic H
2 evolution efficiency was two times higher than that of conventional bulk Ta
3N
5, as a result of the thin-wall morphology. This ordered mesoporous structure had a wall thickness of 2 nm, a pore size of 4 nm, and a surface area as large as 100 m
2·g
−1. Shorter charge migration distance and increased surface active sites contributed to the enhanced efficiency. The same group also reported a precursor route for preparing Ta
3N
5 nanoparticles (Fig. 10(b)) [
85]. Ta
2O
5 nanoparticles, as a precursor for Ta
3N
5, were prepared using a precipitation method. With the particle size decreasing to 30–50 nm, the nanoparticulate Ta
3N
5 showed three times higher H
2 evolution activity than normal Ta
3N
5 (particle size 300–500 nm). The template-assisted method is another method of preparing nanostructured materials. The template not only acts as a model to control the morphology, but also acts as a support to prevent the Ta
2O
5 nanostructures from collapse during nitridation. By adopting mesoporous C
3N
4 as a template, Ta
3N
5 nanoparticles as small as 20 nm were obtained (Fig. 10(c)) [
86]. Decreased particle size and increased surface area shortened the diffusion length of photo-excited electrons and holes, and further improved the charge carrier separation, making the resulting activity a magnitude higher than that of bulk Ta
3N
5. Similar to the silica nanosphere templates mentioned above, polystyrene (PS) spheres are also used as templates to synthesize microporous Ta
3N
5 (Fig. 10(d)) [
87]. The PS sphere templates can easily be removed during calcination. The microporous structure and photonic behavior of the microporous Ta
3N
5 contributed to enhanced photon absorption and better performance [
88,
89].
In addition to nanoparticle and mesoporous structures, the construction of hierarchical nanostructures can effectively promote light harvesting and charge transfer. Hierarchical metastable γ-TaON structures have been reported as efficient H
2 evolution photocatalysts (Fig. 11) [
90]. First, hierarchical Ta
2O
5 was prepared using an
in situ self-assembly wet-chemical method. Next, a high-temperature nitridation process was used to transform Ta
2O
5 into TaON and Ta
3N
5. The hierarchical hollow structure of nano-needles that was assembled not only showed a large specific surface area but also led to multiple light reflections within the chamber. The obtained single-phase γ-TaON hierarchical structures exhibited a H
2 evolution rate of 381.6 µmol·h
−1 and the apparent QE reached 9.5% (420 nm, ~47.5 times higher than that of traditional TaON). The converted Ta
3N
5 also showed improved photocatalytic H
2 evolution activity, reaching as high as 127.5 µmol·h
−1 with an apparent QE of 3.1% (420 nm). The high efficiency is attributed to the synergistic effect of the hierarchical morphology and the crystal and electronic structures.
On the other hand, use of a nanostructured Ta
2O
5 precursor can decrease the nitridation temperature and duration, which contributes to the maintenance of the nanostructure and decreases the amount of the Ta reduced species on the surface. Ordered porous Ta
2O
5 nanostructures were obtained from an ordered porous C
3N
4 template, which was prepared by using close-stacked silica nanospheres as templates [
91]. It is important to note that this ordered porous structured Ta
2O
5 lowered the nitridation temperature, which resulted in a reduced extent of defect sites. Thus, the enhanced photocatalytic activity of the Ta
3N
5 photocatalyst obtained by this method was attributed to decreased defect sites, increased surface area, and efficient light harvesting. Similarly, the use of amorphous and shape-controlled Ta
2O
5 can decrease the nitridation time of Ta
3N
5, leading to fewer surface defects. Amorphous Ta
2O
5 nanoplates and octahedra were synthesized via aerosol-assisted molten salt syntheses (AMSS). The obtained porous Ta
3N
5 nanoplates and octahedra showed enhanced photocatalytic H
2 evolution rate, which could be attributed to suppression of the reduced Ta
5+ surface states and increased surface area (Fig. 12) [
92].
Surface modification
Nanostructures can decrease the distance migrated by the charge carrier and reduce body recombination. However, surface defects normally play the role of recombination centers for photo-excited charge carriers. Therefore, surface charge recombination is one of the major hazards for the photocatalytic performance of tantalum (oxy)nitride-based photocatalysts. However, reducing surface defects has been a challenge for tantalum (oxy)nitride-based photocatalysts [
12]. ZrO
2 was reported to be an effective surface-passivated layer for TaON and Ta
3N
5 [
93–
96]. It was found that a solid solution formed between ZrO
2 and tantalum (oxy)nitride during the nitridation process. The solid solution on the surface could suppress the formation of reduced Ta species. Due to the decrease in reduced Ta species, ZrO
2-modified TaON and Ta
3N
5 photocatalysts showed an enhanced photocatalytic H
2 evolution rate. Another report about BaTaO
2N may further elucidate the positive effect of surface modification [
50]. Through the modification of a BaTaO
x precursor with a Ba-Zr oxide species, a BaZrO
3-BaTaO
2N solid solution formed after nitridation and showed six- to nine-fold enhancement of H
2 evolution without a sacrificial agent. This improved performance resulted from the enlarged bandgap and reduced defect density compared with bare BaTaO
2N, which led to an enhanced driving force for the water redox reaction and reduced charge recombination [
85].
Self-oxidation and the reverse reaction are the main problems that impede the water-splitting activity of tantalum (oxy)nitride-based photocatalysts. A perovskite-type CaTaO
2N photocatalyst was recently produced via appropriate surface modification, and was reported to exhibit overall photocatalytic water splitting (Fig. 13) [
51]. CaTaO
2N has a narrow bandgap and enough bandgap potential for water-splitting reactions (Fig. 13(a)) [
51]. However, surface self-oxidation and the release of N
2 make this photocatalyst unstable. The surface of the CaTaO
2N was modified with a thin layer of titanium oxyhydroxide through photodepostion, which effectively suppressed the surface self-oxidation and the reverse reaction. After loading the co-catalysts for the redox reactions, the modified CaTaO
2N achieved stable overall water splitting (Fig. 13(b)) [
51].
Depositing co-catalysts on the surface of photocatalysts is a general strategy to improve the water-splitting performance. However, surface states often result in the formation of an interface barrier between the co-catalyst and the photocatalyst, which is unfavorable for interfacial charge transfer. Chen et al. [
97] reported that introducing a magnesia nanolayer between Pt nanoparticles and Ta
3N
5 could enhance the photocatalytic H
2 evolution efficiency significantly. The Pt/MgO-Ta
3N
5 photocatalysts reached 22.4 μmol·h
−1 for H
2 evolution, which is about 17 times higher than the activity of the unmodified sample. It was found that the Pt nanoparticles deposited on MgO-Ta
3N
5 had a relatively small particle size and uniform dispersion, which resulted in more active sites and a faster surface reaction (Fig. 14(a, b)) [
97]. This finding was attributed to the passivation of surface defects by MgO and the improvement of surface charge transfer from Ta
3N
5 to Pt. The same group further modified the surface of Ta
3N
5 with barium (Ba) to promote the photocatalytic H
2 evolution rate, as shown in Fig. 14(c) [
98]. It was found that BaTaO
2N formed on the surface of Ta
3N
5 after modification with Ba. BaTaO
2N not only passivated the surface defects but also formed a heterojunction with Ta
3N
5 (Fig. 14(d)) [
98]. The improved photocatalytic H
2 evolution rate should be attributed to the synergetic effect of increased charge separation and decreased surface recombination.
Co-catalysts and heterostructures
Separating the photo-generated electrons and holes in different regions or sites to react with water by loading co-catalysts is an efficient way to increase photocatalytic efficiency [
20,
99–
105]. Co-catalysts, which extract charge carriers from photocatalysts, show high catalytic activity for the water redox reaction. Faster extraction of charge carriers not only reduces bulk recombination but also suppresses the self-oxidation resulting from hole accumulation in the bulk, thereby improving the stability of tantalum (oxy)nitride-based photocatalysts. For example, Ta
3N
5 hollow spheres decorated with spatially separated co-catalysts were prepared with the assistance of silica spheres, and showed improved stability and enhanced H
2 evolution activity (Fig. 15) [
40]. Pt nanoparticles were placed on the inner Ta
3N
5 shell surface as electron collectors, and IrO
2 or CoO
x nanoparticles were loaded on the outer shell surfaces as hole collectors (Fig. 15(a)) [
40]. This hollow structure with separated co-catalysts has two advantages: ① It has an increased surface area and more active sites than bulk Ta
3N
5; and ② separated co-catalysts promote the migration and separation of photo-excited electrons and holes toward the inner and outer surfaces, respectively, thus suppressing recombination and reverse reactions. This system showed significant enhancement for photocatalytic water reduction (Fig. 15(d)) [
40]. Moreover, no N
2 gas was detected during the H
2 evolution process, indicating improved stability.
As mentioned in Section 2.3.3, surface modification with ZrO
2 can suppress reduced Ta defects and enhance the water reduction performance of TaON. Therefore, ZrO
2/TaON was furthered modified with appropriate nanoparticulate co-catalysts for H
2 and O
2 evolutions, resulting in redox reagent-free overall water splitting (Fig. 16) [
18]. As shown in Fig. 16(a) [
18], the overall water-splitting reaction is affected by the synergistic combination of RuO
x, Cr
2O
3, and IrO
2. RuO
x loaded on a ZrO
2/TaON composite promoted both water reduction and oxidation activity [
106]. Due to H
2-O
2 recombination to form H
2O and to the photoreduction of O
2 on the surface of RuO
x, a Cr
2O
3 shell that was permeable for protons and hydrogen, but not oxygen, was loaded onto the surface of RuO
x to prohibit the reverse reactions and make the overall water splitting achievable [
107–
110]. The function of IrO
2 is to improve the stability of the photocatalyst. The authors attributed the improved stability to the promotion of water oxidation by IrO
2, which is known to be the most effective catalyst for O
2 evolution [
111–
113]. Thus, the overall water-splitting reaction on the composite photocatalyst IrO
2/Cr
2O
3/RuO
x/ZrO
2/TaON can provide some useful insight into the reasonable design of a functional co-catalysts/photocatalyst system.
Combining different materials to form heterostructured photocatalysts is another effective strategy to improve water-splitting performance, due to the improvement of photon absorption and charge separation [
5,
11]. Numerous composite photocatalysts, including Cu
2O/TiO
2, TiO
2/CdS, and CdS/WO
3, were combined and showed remarkably improved photocatalytic performance compared with single-component photocatalysts [
114–
117]. Increasing efforts have been made to construct tantalum (oxy)nitride-based heterostructured photocatalysts. Liu et al. [
118] reported a nano Au/Ta
3N
5 composite as a photocatalyst for H
2 generation under visible-light irradiation. The nano Au/Ta
3N
5 composite was prepared through nitridation of Au/Ta
2O
5, which was synthesized via a simple Pechini-type sol-gel process. Gold (Au) nanoparticles with a diameter of 15–20 nm were embedded in the Ta
2O
5 host (Fig. 17(a,b)) [
119]. The prepared nano Au/Ta
3N
5 heterostructures showed remarkably improved H
2 evolution performance under visible-light irradiation compared with pure Ta
3N
5 nanoparticles. The authors attributed the enhanced H
2 evolution activity to the synergetic effect of a near-field electromagnetic effect induced by the surface plasmon resonance of Au nanoparticles (Fig. 17(c)) and charge transfer in the Au/Ta
3N
5 composite. Fig. 17(d) [
119] shows the time course of H
2 evolution for the Au/Ta
3N
5 composite photocatalysts. A certain amount of Au nanoparticles can enhance the photocatalytic H
2 evolution performance, whereas excessive Au nanoparticles may act as recombination centers and impede the photocatalytic H
2 evolution activity [
119].
Heterojunctions formed between two photocatalysts with suitable bandgaps and matched band positions have been demonstrated to be effective for improving photocatalytic performance [
120]. Adhikari et al. [
121] reported the composites of Ta
3N
5 or TaON with Bi
2O
3 to have enhanced visible-light-driven H
2 evolution activity. They ascribed the increased visible-light activity for Ta
3N
5 or TaON to the trapping of holes by Bi
2O
3. Under visible-light irradiation, both Ta
3N
5 and Bi
2O
3 were excited to generate electrons and holes. The electrons from Ta
3N
5 or TaON took part in the H
2 evolution activity and holes were recombined with the electrons from Bi
2O
3, similar to the Z-scheme mechanism shown in Fig. 18 [
121]. In other words, the enhanced H
2 evolution activity of Bi
2O
3/Ta
3N
5 or Bi
2O
3/TaON composites could be attributed to improved charge separation [
121].
As the bandgaps of most tantalum (oxy)nitride-based photocatalysts straddle water redox potentials, tantalum (oxy)nitride-based photocatalysts can act as both H
2 evolution photocatalysts (HEPs) and as O
2 evolution photocatalysts (OEPs) in a Z-scheme system. For example, Higashi et al. [
122] designed a Z-scheme system with TaON photocatalysts to achieve visible-light overall water splitting. As shown in Fig. 19(a) [
122], the TaON acted as both HEP and OEP after the loading of appropriate co-catalysts. With the assistance of an
/I
– redox mediator, the Pt/TaON (HEP) and RuO
2/TaON (OEP) mixtures reacted with water to produce H
2 and O
2 under visible-light irradiation. Later, Tabata et al. [
123] further decorated the surface of Ta
3N
5 with rutile titania (R-TiO
2), which acted as an OEP in a two-step water-splitting system (Fig. 19(b)). After the loading of iridium (Ir) nanoparticles, Ir/R-TiO
2/Ta
3N
5 achieved visible-light overall water splitting along with Pt/ZrO
2/TaON as a HEP, assisted by an
/I
– redox mediator. It was believed that the decorated R-TiO
2 hindered the adsorption of I
– on Ta
3N
5, while the Ir nanoparticles played the role of active sites to reduce
to I
–, thereby allowing Ta
3N
5 to evolve O
2 in the two-step water-splitting system.
Performance of tantalum (oxy)nitride-based photocatalysts
To improve the water-splitting efficiency, great effort has been focused on each step of the photocatalytic process, including photon absorption, charge separation and migration, and surface reaction. The main strategies—doping, morphological control, surface modification, co-catalysts, and heterostructures—are discussed above. High activity and stability for photocatalysts are based on the synergistic effect of these steps. Photocatalytic overall water splitting has been achieved on modified TaON, CaTaO
2N, and LaMg
xTa
1–xO
1+3xN
2–3x. Table 2 [
18,
21,
40,
43,
51,
63,
65,
81,
84,
87,
90,
92,
96–
99,
118,
119] summarizes and compares relevant studies on this topic. It is clear that nanostructures show relatively higher H
2 evolution performance due to the increased number of active sites and the short charge transfer distance. In addition, heteroatoms-doping that is based on bandgap engineering is an effective strategy to enhance the H
2 evolution performance of tantalum (oxy)nitride-based photocatalysts. However, a greater surface area means more surface defects, which not only act as recombination centers but also impede the photo-excited charge transfer between the photocatalyst and the co-catalyst. Also, the heteroatom dopant may act as a recombination center. Thus, surface modification seems to be a more powerful strategy for the improvement of the H
2 evolution performance of tantalum (oxy)nitride photocatalysts.
Conclusions and outlook
Tantalum (oxy)nitride-based photocatalysts, which have a narrow bandgap for visible-light absorption and suitable bandgap edges for the water redox reaction, are regarded as a class of promising candidates for water splitting. Because they have much lower water reduction capability than water oxidation capability, considerable attention has been devoted to the improvement of the photocatalytic H2-generation efficiency of tantalum (oxy)nitride-based photocatalysts. Surface states are considered to be a major factor influencing photocatalytic water-splitting activity. Surface defects caused by nitrogen vacancies and Ta reduced species act as recombination centers and impede the surface charge transfer and reaction. In addition, self-oxidation and the reverse reaction during a photocatalytic reaction make these photocatalysts unstable. In order to improve the water-splitting performance of tantalum (oxy)nitride-based photocatalysts, many strategies have been adopted, including doping, morphology control, surface modification, co-catalysts, and heterostructures design. These strategies work by improving charge separation, charge migration, and surface reactions. Photocatalytic overall water splitting has been achieved on some tantalum (oxy)nitride-based photocatalysts. In addition, the stability of tantalum (oxy)nitride-based photocatalysts has been significantly improved with appropriate co-catalyst design and surface modification.
To further improve the photocatalytic overall water-splitting efficiency of tantalum (oxy)nitride-based photocatalysts, increased attention should be paid to better designing and utilizing the synergistic effect of various strategies. The following key points should be considered in future research.
(1) Defects control. It is believed that most defects on the surface or in the bulk will act as recombination centers for photo-excited electrons and holes. Moreover, surface defects may generate interfacial barriers between the photocatalysts and the co-catalysts, and impede charge transfer. It is very important but quite challenging to reduce the defects because of the harsh nitridation conditions. It is easy to introduce nitrogen vacancies and Ta reduced species during the high-temperature nitridation process in a NH3 atmosphere. The exploration of new precursors and synthesis methods under mild conditions is necessary in order to reduce the defects of tantalum (oxy)nitride-based photocatalysts.
(2) Morphology control. The morphology of photocatalysts is a key factor that influences light absorption, charge migration, and surface reaction. Nanotechnology has been intensively used to design various photocatalysts, and for the most important aspect of morphology control. Reducing the particle size to the nanoscale results in a shorter migration distance that makes more charge carriers move to the surface before recombination. Furthermore, nanostructures decrease the temperature and duration of nitridation, which reduces defects such as nitrogen vacancies and Ta reduced species. In addition, ordered porous nanostructures increase light absorption because of the photonic effect. An ordered hierarchical structure will provide room for improving the water-splitting activity of tantalum (oxy)nitride-based photocatalysts.
(3) Co-catalyst design. Loading co-catalysts is an effective approach to improve photocatalytic performance. Tantalum (oxy)nitride-based photocatalysts suffer from self-oxidation during the photocatalytic process, as a result of the poor extraction of photo-generated holes. The loading of a co-catalyst for water oxidation can promote the extraction of holes and improve the stability of photocatalysts. Precise control of the particle size and dispersion of co-catalysts should show a positive effect on the stability and performance of the photocatalyst. Thus far, Pt is the most-used H2 evolution co-catalyst for Ta3N5 based photocatalysts. However, due to its rarity and high cost, Pt is not favorable for scale-up applications. Therefore, the development of other earth-abundant co-catalysts for H2 evolution is greatly welcome.
In conclusion, much effort has been made to improve the water-splitting efficiency of tantalum (oxy)nitride-based photocatalysts, and great progress has been achieved over the past years. Due to the synergetic effect of light harvesting, charge separation and migration, and surface reaction during the photocatalytic water-splitting process, more research attention should be paid to combining strategies into multi-strategies. Persistent efforts in this area are expected to realize highly efficient overall water splitting on these photocatalysts. Furthermore, the knowledge and understanding of mechanisms that have been acquired from studying these materials will shed light on the development of other new, efficient, and sustainable photocatalysts. For the future development of photocatalytic water splitting, unified evaluation standards and criteria for overall photocatalyst performance, including efficiency and stability, are urgently required to allow this research community to achieve its ambition of long-term sustainable solar fuel production.
THE AUTHORS. Published by Elsevier LTD on behalf of the Chinese Academy of Engineering and Higher Education Press Limited Company. This is an open access article under the CC BY-NC-ND license (http://creativecommons.org/licenses/by-nc-nd/4.0/).