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Toward the Creation of Highly Active Photocatalysts That Convert Methane into Methanol

By Yuichi Negishi, Seiichiro Watanabe, Marika Aoki, Sakiat Hossain and Wataru Kurashige

Submitted: February 5th 2019Reviewed: February 20th 2019Published: March 21st 2019

DOI: 10.5772/intechopen.85335

Downloaded: 184

Abstract

Methane exists abundantly around Japan as methane hydrate. As the effective use of such methane, the conversion of methane into methanol has recently attracted much attention. Photocatalytic reaction is one of the methods which convert methane into methanol without using much energy. However, it is indispensable to improve the photocatalytic activity for their practical use. Our group has attempted to improve the activity of mesoporous tungsten trioxide and titanium dioxide (m-WO3 and m-TiO2) photocatalysts, which convert methane into methanol, by loading the ultrafine metal clusters as cocatalyst on the photocatalysts. As a result, we have succeeded in loading ultrafine metal-cluster cocatalysts onto m-WO3 and m-TiO2 and thereby improving their photocatalytic activity. Our study also demonstrated that the kind of metal element suitable for each photocatalyst depends on the kind of the photocatalysts, and thereby it is important to select the metal clusters suitable for each photocatalyst for improving its photocatalytic activity.

Keywords

  • photocatalyst
  • methane
  • methanol
  • activation
  • cocatalyst

1. Introduction

In recent years, the effective use of methane (CH4) has attracted attention owing to the large amount of methane hydrate which is estimated to exist under the sea around Japan (Figure 1(a)) [1]. When CH4 is burnt for generating energy, it generates small amounts of compounds which cause environmental problems, such as carbon dioxide, nitrogen oxide, and sulfur oxide (Figure 1(b)), [2]. Therefore, CH4 can be used as a comparatively clean energy source. However, since CH4 is a gas state at room temperature, it occupies a large volume and therefore costs for the transportation. On the other hand, if CH4 is converted to liquid methanol (CH3OH), the transportation costs could be reduced. Furthermore, the generated CH3OH could be effectively used as a raw material for producing various chemical compounds. Therefore, in recent years, considerable attention has been focused on the development of a methodology for efficiently converting CH4 into CH3OH.

Figure 1.

(a) Estimated distribution of methane hydrate lying under the sea around Japan. (b) emission rate of each gas (CO2, NOx, or SOx) from CH4, petroleum, and coal. In (b), emission rate of each gas is normalized by letting the emission rate of CO2 from coal be 100. Adapted from [1, 2].

Regarding such a conversion, the current main methods require extreme conditions such as high temperature of around 500°C and high pressure of 50 atm or more [3]. Furthermore, since the reaction proceeds in two stages, the conversion consumes a large amount of energy. Therefore, many studies have been conducted to find a method for the direct conversion of CH4 to CH3OH under mild conditions. However, most direct reactions require also high temperature and pressure conditions together with the use of an oxidizing agent [4]. Using a photocatalytic reaction for this conversion, the reaction can be conducted under moderate conditions [5]. However, the catalytic activity is still low, and further improvement is required for practical application. Then, our group has attempted to improve the photocatalytic activity of the photocatalyst used in this conversion. Our strategy was to load the controlled metal clusters on the surface of the photocatalyst as active sites (cocatalyst).

2. Research examples

Both tungsten oxide (WO3) and titanium oxide (TiO2) have redox potentials that are sufficient to generate hydroxyl radicals (·OH) (Figure 2(a)), which is necessary for the reaction to proceed (Figure 2(b)) [6]. Furthermore, in their mesoporous structures (m-WO3 and m-TiO2), surface area becomes large and thereby the adsorption of reactive molecules is enhanced. In addition, in m-WO3 and m-TiO2, since the regular arrangement of pores suppresses the recombination of electrons and holes generated by the light irradiation, electrons and holes can be efficiently used in the reaction [7]. Then, in our study, we attempted to activate such m-WO3 and m-TiO2 by loading the ultrafine metal clusters as cocatalyst on the photocatalysts.

Figure 2.

(a) Redox potentials of WO3 and TiO2. Adapted from [4]. (b) Mechanism of the conversion of CH4 to CH3OH by photocatalytic reaction; C.B., V.B., and Eg indicate conduction band, valence band, and band gap, respectively.

2.1 m-WO3 photocatalyst

2.1.1 Preparation and loading of cocatalyst

m-WO3 was prepared using a hard template method in the same manner as that reported in the literature [8]. First, mesoporous silica (KIT-6) was prepared to be used as a template (Figure 3(a)). Then, the obtained KIT-6 was mixed with 12-tungsto(VI)phosphoric acid n-hydrate (H3(PW12O40)∙nH2O) in ethanol. The product was dried and then calcined at 350°C for 4 h. To the obtained powder, a further H3(PW12O40)∙nH2O ethanol solution was added and the mixture was stirred for 30 min. The product was again dried and then calcined at 550°C for 6 h. Finally, m-WO3 was obtained by removing the KIT-6 template using hydrofluoric acid (HF) (Figure 3(b)).

Figure 3.

Preparation methods of (a) KIT-6, (b) m-WO3, and (c) Mn-m-WO3 (M = Ag, Ni, or Co).

Next, metal clusters were loaded onto the obtained m-WO3. Our previous research on water-splitting photocatalysts [9, 10, 11, 12, 13] revealed that when a chemically-synthesized ligand-protected metal cluster is adsorbed onto a photocatalyst and its ligand is removed by the calcination, the controlled metal clusters can be loaded on the photocatalyst. Then, in this study, each metal cluster was loaded onto m-WO3 using such a method (Figure 3(c)). Silver (Ag), nickel (Ni), and cobalt (Co) were chosen as metal element because they were expected to work as cocatalyst [14, 15]. Glutathionate (SG) was used as the ligand of the metal cluster. SG-protected silver clusters (Agn(SG)m) were synthesized using the solid phase method reported by Bakr et al [16]. Nin(SG)m and Con(SG)m clusters were synthesized using the liquid phase method reported for SG-protected gold clusters (Aun(SG)m) [17]. The Mn(SG)m clusters (M = Ag, Ni, or Co) thus obtained were dissolved in water, and m-WO3 was added to this solution to adsorb the Mn(SG)m clusters on m-WO3 (Mn(SG)m-m-WO3; M = Ag, Ni, or Co). The obtained Mn(SG)m-m-WO3 was calcined at 500°C under atmospheric pressure to remove the ligand of the Mn(SG)m cluster, and thereby, each metal cluster was loaded on m-WO3 (Mn-m-WO3; M = Ag, Ni, or Co).

2.1.2 Structural characterization

In the transmission electron microscope (TEM) image of m-WO3, pores of 10 nm or less were observed (Figure 4(a,b)). In the small angle X-ray diffraction (XRD) pattern of m-WO3 (Figure 4(c)), similar to the literature [18], a peak assigned to the (211) plane of KIT-6 was observed, in addition to the peak attributed to the (110) plane derived from cubic I4132 or I4332. These results indicate that the synthesized m-WO3 has an arranged structure with regular pores.

Figure 4.

Characterization of m-WO3. (a) TEM image, (b) expanded TEM image, and (c) small angle XRD pattern.

Figure 5(a,b) shows the TEM images of Con(SG)m-m-WO3 and Con-m-WO3, respectively, as representative examples of photocatalysts after adsorption and calcination. Particles with a size of 0.93 ± 0.20 nm could be observed in the TEM image of Con(SG)m-m-WO3. This indicates that ultrafine Con(SG)m clusters were synthesized with a narrow distribution. Particles of a similar size (0.96 ± 0.19 nm) were also observed for Con-m-WO3. This indicates that Con clusters were loaded onto m-WO3 during calcination without the aggregation. Based on the bulk density of Co (8.900 g/cm3), it can be estimated that each loaded particle contains about 40 Co atoms. The loading of ultrafine particles was similarly observed in other Mn-m-WO3 (M = Ag or Ni). In this way, we have succeeded in loading ultrafine Mn clusters on m-WO3 with a narrow size distribution.

Figure 5.

TEM image and particle size distribution of (a) Con(SG)m-m-WO3 and (b) Con-m-WO3. Multiple ultrafine particles can be seen in the white circles.

2.1.3 Evaluation of photocatalytic activity

The photocatalytic activity was measured using an experimental apparatus built in-house consisting of a high-pressure mercury (Hg) lamp (400 W) and a quartz cell (Figure 6) [11]. First, 300 mg of Mn-m-WO3 (M = Ag, Ni, and Co) was dispersed in 300 mL of water. Then, CH4 and helium carrier gas were passed through this solution at a flow rate of 4.5–5 mL/min and 18 mL/min, respectively. The reaction was performed by the irradiation of ultraviolet light using a high-pressure Hg lamp. The temperature of the reaction system was maintained at 55–60°C by a circulator, and the gas generated by the reaction was analyzed with gas chromatography.

Figure 6.

Experimental apparatus built in-house consisting of a high-pressure mercury (Hg) lamp (400 W) and a quartz cell. GC means gas chromatograph.

Figure 7 shows the rate of CH3OH evolution from an aqueous solution containing Mn-m-WO3 or m-WO3. All the photocatalysts loaded with Mn clusters evolved CH3OH at faster rate as compared with m-WO3 without cocatalyst. This indicates that the loading of the Mn clusters improved the rate of the conversion of CH4 to CH3OH. It was found that the Con clusters have the largest improvement effect among the Mn clusters used in this study.

Figure 7.

Rate of CH3OH evolution from an aqueous solution containing Mn-m-WO3 or m-WO3.

According to a previous study on m-WO3 [8], in the conversion of CH4 to CH3OH, first, the holes generated via photoexcitation oxidize the hydroxyl groups (OH) on the photocatalyst surface and/or water (H2Oad) adsorbed on the surface to form ·OH radicals. The ·OH radicals have intense oxidizing power and attack CH4 to generate methyl radicals (·CH3). The ·CH3 radicals thus produced react with H2O to produce CH3OH (Figure 2(b)). It can be considered that loading Mn clusters onto m-WO3 promotes the charge separation between the electrons and holes, and thereby, the holes are efficiently consumed [15], leading to the improvement of the activity. It is presumed that highest activity was observed in the reaction using Con-m-WO3, since the relationship between the positions of valence band of the photocatalyst and the orbitals of the loaded Mn cluster and/or the relationship between the redox potential of ·OH radical and that of the loaded Mn cluster was effective for accelerating the reaction in Con-m-WO3 compared with the other photocatalysts (Agn-m-WO3 or Nin-m-WO3).

2.2 m-TiO2 photocatalyst

2.2.1 Preparation and loading of cocatalyst

A m-TiO2 photocatalyst was prepared according to a method reported in the literature [19]. Specifically, m-TiO2 photocatalyst was prepared by forming a photocatalyst around the micelle composed of surfactants. First, hexadecyltrimethylammonium bromide ([(C16H33)N(CH3)3]Br) was added to an aqueous solution of titanyl oxysulfate sulfuric acid hydrate (TiOSO4), and the solution was stirred at 60°C for 24 h. The obtained precipitate was washed with water and dried at 120°C for 10 h. Then, the dried sample was calcined at 450°C for 2 h to obtain m-TiO2 (Figure 8). The Mn clusters (M = Ag, Ni, or Co) were loaded onto the surface of the obtained m-TiO2 using the same method as that described for Mn-m-WO3 (Figure 3(c)).

Figure 8.

Preparation methods of m-TiO2.

2.2.2 Structural characterization

Figure 9(a) shows a TEM image of the prepared m-TiO2. It can be confirmed from this image that the material has a mesoporous structure different from that of m-WO3 (Figure 4(b)). The diffuse reflection (DR) spectrum of m-TiO2 revealed that the obtained m-TiO2 has a band gap of around 3.24 eV, indicating that the obtained m-TiO2 has an anatase type structure [19].

Figure 9.

Characterization of m-TiO2. (a) TEM image and (b) DR spectrum.

Figure 10(a) shows a TEM image of the Nin(SG)m cluster, as a representative example of a synthesized Mn(SG)m cluster. The particles with a size of 0.70 ± 0.14 nm can be observed in Figure 10(a). On the other hand, the particles with a slightly larger size of 0.92 ± 0.17 nm were observed in the TEM image of Nin-m-TiO2 (Figure 10(b)). This indicates that, in the synthesis of Nin(SG)m-m-TiO2, some cluster aggregation occurred during the adsorption or calcination processes. However, the size distribution of the observed particles is very narrow even for loaded particles. The number of Ni atoms contained in each particle was estimated to be about 40, based on the bulk density of Ni (8.908 g/cm3). Loading of such ultrafine particles was similarly observed for the other Mn-m-TiO2 (M = Ag or Co). These results indicate that m-TiO2 ultrafine clusters were successfully loaded on a photocatalyst with a narrow distribution of the particle size.

Figure 10.

TEM image and particle size distribution of (a) Nin(SG)m and (b) Nin-m-TiO2.

2.2.3 Evaluation of photocatalytic activity

The photocatalytic activity of a series of Mn-m-TiO2 obtained in this manner was estimated in the same manner as that described in Section 2.1.3. Figure 11 shows the rate of CH3OH evolution from aqueous solutions containing either Mn-m-TiO2 or m-TiO2. Overall, the rate of CH3OH evolution from Mn-m-TiO2 or m-TiO2 was lower than that from Mn-m-WO3 or m-WO3. Since the position of conduction band is relatively high in TiO2 (Figure 2(a)), the superoxide radicals with strong oxidizing power can be generated from aqueous solution containing Mn-m-TiO2 or m-TiO2 by photoirradiation. It can be considered that since the superoxide radicals such generated attacked CH3OH and thereby the excessive oxidation (decomposition) of CH3OH occurred [20], the rate of the CH3OH evolution decreased as a whole in the case of Mn-m-TiO2 or m-TiO2 compared to the case of Mn-m-WO3 or m-WO3. Figure 11 also revealed that the loading of Mn clusters has the effect of promoting the conversion of CH4 into CH3OH also in the case of Mn-m-TiO2.

Figure 11.

Rate of CH3OH evolution from an aqueous solution containing Mn-m-TiO2 or m-TiO2.

On the other hand, regarding the metal elements, Ni showed a particularly high cocatalytic effect in Mn-m-TiO2, unlike the case of m-WO3 (Figure 11). The relationship between the position of the valence band of the photocatalyst and the position of the orbitals of the loaded Mn cluster and/or the relationship between the redox potential of ·OH radical and that of the loaded Mn cluster are considered to be strongly related to these phenomena. These results indicate that choosing an appropriate cocatalyst depending on the type of photocatalyst is very important to improve the photocatalytic activity.

3. Conclusions

Ultrafine Mn clusters (M = Ag, Ni, or Co) with a particle size of around 1 nm were successfully loaded onto m-WO3 and m-TiO2 with a narrow distribution. The photocatalytic activity measurements clearly demonstrated that the loading of such cocatalysts is effective in improving the activity for both types of photocatalysts. Furthermore, our study also revealed that it is important to appropriately selecting the element of the cocatalyst according to the photocatalyst to improve the photocatalytic activity. In these experiments, the particle diameter of the cocatalyst was reduced to approximately 1 nm to increase the reactive surface area. However, this size of a cocatalyst particle might not be optimal for promoting the reaction. In fact, our previous studies on water-splitting photocatalysts showed that extreme refining of the cocatalyst particles reduces the activity per a surface atom of cocatalysts [8]. Therefore, in future studies, we would like to clarify the correlation between the particle size and activity of the cocatalyst. Furthermore, it seems also necessary to consider the method for efficiently consuming the excited electrons to accelerate the reaction.

Acknowledgments

We thank Mr. Shun Yoshino for technical assistance. This work was supported by the Japan Society for the Promotion of Science (JSPS) KAKENHI (grant numbers JP16H04099 and 16 K21402), Scientific Research on Innovative Areas “Coordination Asymmetry” (grant number 17H05385), and Scientific Research on Innovative Areas “Innovations for Light-Energy Conversion” (grant number 18H05178). Funding from the Takahashi Industrial and Economic Research Foundation, Futaba Electronics Memorial Foundation, Iwatani Naoji Foundation, and Asahi Glass Foundation is also gratefully acknowledged.

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Yuichi Negishi, Seiichiro Watanabe, Marika Aoki, Sakiat Hossain and Wataru Kurashige (March 21st 2019). Toward the Creation of Highly Active Photocatalysts That Convert Methane into Methanol [Online First], IntechOpen, DOI: 10.5772/intechopen.85335. Available from:

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