Kazuhiko
Maeda
*a,
Ryo
Kuriki
a,
Mingwen
Zhang
b,
Xinchen
Wang
b and
Osamu
Ishitani
a
aDepartment of Chemistry, Graduate School of Science and Engineering, Tokyo Institute of Technology, 2-12-1-NE-2 Ookayama, Meguro-ku, Tokyo 152-8550, Japan. E-mail: maedak@chem.titech.ac.jp
bState Key Laboratory of Photocatalysis on Energy and Environment, College of Chemistry, Fuzhou University, Fuzhou 350002, P. R. China
First published on 21st July 2014
Carbon nitride (C3N4) polymers work as a vital component in a photocatalytic CO2 reduction assembly that operates under visible light when modified with a ruthenium complex, trans(Cl)-[Ru{4,4′-(CH2PO3H2)2-2,2′-bipyridine}(CO)2Cl2], (Ru) as a catalyst. Here we examined the effects of structural properties of carbon nitride on the photocatalytic performance for CO2 reduction into formic acid. Introduction of mesoporosity into the graphitic carbon nitride structure increased the specific surface area, leading to significant enhancement in activity. However, higher surface area (in other words, lower crystallinity) that originated from excessively introduced mesopores had a negative impact on activity, although it is a prerequisite to allow for adsorption of Ru on the carbon nitride surface. Thus, the activity was sensitive to specific surface area and crystallinity of carbon nitride, but is largely insensitive to the pore size and the volume.
Our group has very recently reported that photocatalytic CO2 reduction was achieved using a composite of a ruthenium complex, trans(Cl)-[Ru{4,4′-(CH2PO3H2)2-2,2′-bipyridine}(CO)2Cl2] (abbreviated as Ru), and mesoporous graphitic carbon nitride (mpg-CN) with visible light in the presence of triethanolamine that works as an electron donor and a proton source.14 Importantly, isotope-labelling experiments showed that the products obtained during the reaction originate not from the decomposition of C3N4 itself but from CO2 being used as the reactant. Although the number of papers that describe photocatalytic reactions on carbon nitride has been increasing since the initial report in 2009,16 most of them focus on hydrogen evolution from an aqueous solution containing sacrificial electron donors and/or the decomposition of organic substrates,17 and there are very few that describe photocatalytic CO2 reduction on carbon nitride with sufficient reliability. Our study14 was the first successful example of achieving CO2 reduction through the use of CN-based polymers with visible light. Note here that our system works at ambient pressure and room temperature, in contrast to the previous CO2 thermal activation and conversion scheme using carbon nitride that requires pressurized conditions (3–10 bar) and an elevated temperature (423 K).18
In this hybrid system, electrons and holes are generated in the conduction and valence bands of mpg-CN, respectively, under visible light irradiation (λ > 400 nm). The scheme of the reaction is depicted in Fig. 1. Upon photoexcitation of mpg-CN with visible light, electrons and holes are generated in the conduction band and valence band, respectively. The conduction band electrons move to adsorbed Ru molecules, thereby reducing CO2 into formic acid. Holes left in the valence band are, on the other hand, consumed by electron-donating species such as triethanolamine, and thus establishing the catalytic redox cycle. As this reaction is triggered by visible light absorption of mpg-CN, it is expected that the physicochemical properties, especially pore-wall chemistry of the material, have a significant impact on activity. The structure–activity relationship has been investigated in many different photocatalytic reactions with respect to various types of semiconductors, especially for water splitting.19 It should be stressed that in the heterogeneous photocatalysis research for CO2 reduction, however, such structural effects have not been investigated in detail not only for carbon nitride but also traditional metal-based semiconductor photocatalysts.17 Carbon nitride is one of the most studied semiconductor photocatalysts in recent years. Therefore, uncovering new functionalities of the material is an important mission in materials chemistry.
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Fig. 1 A schematic illustration of photocatalytic CO2 reduction on the Ru/C3N4 composite under visible light illumination. |
In our previous communication,14 we have briefly described photocatalytic CO2 reduction using Ru and mpg-CN. However, no guideline for further improvement in the activity of this system has been established to date. In this study, photocatalytic activity of the Ru/CN composites for visible-light CO2 reduction was examined with respect to the pore-wall structure of CN polymers. Factors affecting the activity are discussed on the basis of the results of structural analyses and photocatalytic reactions.
Fig. 3A shows nitrogen adsorption/desorption isotherms of mpg-CN prepared at different SiO2/cyanamide ratios using 12 nm colloidal SiO2 as the hard template. The curves exhibit a hysteresis typical of a material having randomly connected spherical pores. The specific surface areas increased from 50 to 240 m2 g−1 with an increase in the SiO2/cyanamide ratio in the synthesis, as listed in Table 1. Pore size distribution curves obtained through the BJH (Barrett–Joyner–Halenda) method are shown in Fig. 3B. The result indicated that the increasing SiO2/cyanamide ratio enlarged the pore volume in the mpg-CN structure, while maintaining the peak position of the pore size distribution (11–12 nm).
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Fig. 3 (A) Nitrogen adsorption/desorption isotherms of mpg-CN samples prepared with different SiO2/cyanamide ratios using 12 nm SiO2. (B) The corresponding BJH pore size distributions. |
Entry | Sample | Specific surface area/m2 g−1 | Pore volume/cm3 g−1 | Pore diameter/nm | Amount of formic acid produced/nmol |
---|---|---|---|---|---|
a Reaction conditions: photocatalyst, Ru (3.9 μmol g−1)-loaded C3N4 8.0 mg; solution, a mixture of acetonitrile and triethanolamine (4![]() ![]() |
|||||
1 | g-CNb | 6.1 | — | — | Trace |
2 | CN-12-0.2 | 54 | 0.20 | 12.2 | 1127 |
3 | CN-12-0.5 | 105 | 0.37 | 12.2 | 1854 |
4 | CN-12-1.0 | 200 | 0.64 | 10.7 | 1561 |
5 | CN-12-1.5 | 240 | 0.74 | 10.7 | Trace |
6 | CN-7-1.0 | 241 | 0.51 | 7.2 | Trace |
7 | CN-24-1.0 | 130 | 0.70 | 24.4 | 1223 |
Using colloidal SiO2 nanoparticles having different sizes but with the same SiO2/cyanamide ratio, mpg-CN samples were prepared in a similar manner. Nitrogen adsorption/desorption isotherms shown in Fig. 4A indicated that an uptake of nitrogen adsorbed due to capillary condensation shifted to higher relative pressures as the size of the SiO2 template increased. This is reasonable, considering the fact that the pore size of the materials thus obtained increased with an increase in the SiO2 size, as shown in Fig. 4B. The result of nitrogen adsorption measurements is consistent with that of XRD; that is, introduction of mesoporosity into the g-CN structure results in the loss of long-range atomic ordering.
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Fig. 4 (A) Nitrogen adsorption/desorption isotherms of mpg-CN samples prepared with SiO2 having different sizes (SiO2/cyanamide ratio = 1.0). (B) The corresponding BJH pore size distributions. |
On the basis of these results, we concluded that mpg-CN samples with controlled porosity and pore size were successfully prepared by changing the size of colloidal SiO2 and the mixed ratio of SiO2 and cyanamide. The light-harvesting properties of the mpg-CN samples were investigated by means of UV-visible diffuse reflectance spectroscopy. As shown in Fig. 5, all samples exhibit a steep absorption edge at around 450 nm, which is due to band gap transition of electrons from the N2p valence band to the conduction band formed mainly by C2p orbitals, identical to g-CN.16 As shown in Fig. 5A, the absorption edge shifted slightly to shorter wavelengths with increasing mesoporosity. The same trend was observed in CN samples that have different pore diameters (Fig. 5B). It is also noted here that an absorption tail extending to 600 nm, attributable to surface defective sites, tends to be more pronounced with an increase in mesoporosity. It suggests that the introduction of mesoporosity increased the number of defective sites in the CN structure. This is reasonable considering the increased specific surface area of mpg-CN.
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Fig. 6 Cyclic voltammograms of Ru in DMF/TEOA (4![]() ![]() |
As indicated by our previous work, Ru does not have any noticeable absorption in the visible light region.14 Under >400 nm irradiation, therefore, only the carbon nitride component is excited by visible photons. Actually, Ru-loaded Al2O3 was found to give any carbon-containing product under the present reaction conditions.14 We first tried to compare the activity of g-CN with those of mpg-CN samples using the same amount of Ru. Mpg-CN samples tested in this study were capable of adsorbing Ru (3.9 μmol g−1) quantitatively, but bulk g-CN showed inferior affinity with the complex. As a result, g-CN showed negligible activity for the CO2 reduction reaction. In the edge of the graphitic plane in carbon nitride, there are –NH2 functional groups that work as hydrogen-bonding motifs.21 Obviously, the density of this motif should be increased with an increase in the density of the edge-plane; in other words, the specific surface area. This idea could qualitatively explain the difference in adsorption affinity between g-CN and mesoporous analogues, as the former has much lower specific surface area (6.1 m2 g−1) than the latter (∼240 m2 g−1). Fig. 7 shows a typical FT-IR spectrum of Ru/mpg-CN. The position of two peaks, assigned to the vibration mode of two carbonyl groups, in Ru/mpg-CN was the same as that in Ru dissolved in a KBr pellet. This result indicates that there is little electronic interaction between the adsorbed Ru and mpg-CN. This would be reasonable, considering –CH2– spacers between phosphoric acid groups and a bpy ligand cleaves electronic conjugation. The IR data also indicate that no significant change in the molecular structure of Ru occurred even after fixation onto the surface of mpg-CN; if an appreciable change such as ligand substitution occurs in Ru after adsorption, the positions of the vibration mode of two carbonyl groups should undergo a change more or less. On the basis of the experimental results, a possible form of linkage between the adsorbed Ru and mpg-CN is hydrogen-bonding that would be formed between –NH2 groups and the phosphonate anchors in Ru.
The results of photocatalytic CO2 reduction using mpg-CN samples are listed in Table 1. The activity for the production of formic acid was dependent strongly on the SiO2/cyanamide ratio as well as the size of the SiO2 template. Introduction of mesoporosity by increasing the ratio resulted in improvement of activity (entries 1–5). The fact that turnover numbers by far exceeded 1 (36–59 with respect to Ru) indicated catalytic cycles of the reactions. Interestingly, however, CN-12-1.5, which had the largest pore volume and specific surface area, showed little photocatalytic activity, despite its good affinity with Ru, as mentioned earlier. We also conducted control experiments to make sure that C3N4, Ru, CO2, and triethanolamine are all required to achieve appreciable formic acid formation. No reaction took place in the dark as well. In addition, it was confirmed that no HCOOH was detected when unmodified CN samples were used, indicating that there was no source of HCOOH, including the decomposition of the material itself, in these samples.
Changing the pore size also had a significant impact on activity. CN-7-1.0, which had the smallest pore size distribution and the largest specific surface area, showed negligible activity for the reaction. The performance of CN-24-1.0 having the largest pore diameter and the volume was slightly lower than that of CN-12-1.0. The highest performance was obtained with a sample prepared using 12 nm SiO2 with the SiO2/cyanamide ratio of 0.5–1.0.
We have previously reported the conduction band potentials of g-CN and mpg-C3N4,14,17b which are −1.46 and −1.29 V vs. Ag/AgCl at pH 6.6, respectively. They can be converted to −1.82 and −1.65 V vs. Ag/AgNO3, respectively. It is thus clear that electron transfer from the conduction band of CN materials to Ru, which has the first reduction potential of ca. −1.57 V, is energetically possible. One may also think that the more negative conduction band potential of g-CN than mpg-CN is more favorable for the CN-to-Ru electron transfer. However, the CO2 reduction activity of g-CN was negligibly low, compared to that of mpg-CN (entry 1). This again supports the importance of the mesoporous structure for efficient charge utilization and the subsequent CO2 reduction event.
It should be noted that CN-24-1.0, which has relatively large pore volume, showed activity for the reaction (entry 7). Judging from the reaction data using CN-12-1.5 (entry 5) that has almost the same pore volume (∼0.7 cm3 g−1) as CN-24-1.0 but with much larger surface area, the activity appears to be largely insensitive to the pore volume, but is related to the specific surface area. In other words, there is a trade-off between activity and specific surface area. A larger specific surface area is actually important in terms of adsorption of the Ru catalyst as well as the distance of electron–hole migration, but can lead to more chance to electron–hole recombination.
Ru was adsorbed onto the surface of C3N4 at room temperature. C3N4 (50 mg) was dispersed in methanol (25 mL) containing an appropriate amount of Ru under continuous stirring in the dark to establish adsorption/desorption equilibrium. After 20–24 h, the solid was separated from the suspension by filtration, and the resulting supernatant was then analysed by using a UV-visible spectrometer (Jasco, V-565). The amount of Ru adsorbed was calculated from the difference in absorbance between the initial solution and the supernatant. The resulting solid sample was washed with methanol several times, and was dried under vacuum at room temperature overnight. The amount of Ru loading was 3.9 μmol g−1 unless otherwise stated. The coverage of Ru (3.9 μmol g−1) on mpg-CN having specific surface areas of 50–240 m2 g−1 corresponds approximately to 0.6–2.9%.
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