Recent Advances in Photocatalytic Oxidation of Methane to Methanol

Methane is one of the promising alternatives to non-renewable petroleum resources since it can be transformed into added-value hydrocarbon feedstocks through suitable reactions. The conversion of methane to methanol with a higher chemical value has recently attracted much attention. The selective oxidation of methane to methanol is often considered a “holy grail” reaction in catalysis. However, methanol production through the thermal catalytic process is thermodynamically and economically unfavorable due to its high energy consumption, low catalyst stability, and complex reactor maintenance. Photocatalytic technology offers great potential to carry out unfavorable reactions under mild conditions. Many in-depth studies have been carried out on the photocatalytic conversion of methane to methanol. This review will comprehensively provide recent progress in the photocatalytic oxidation of methane to methanol based on materials and engineering perspectives. Several aspects are considered, such as the type of semiconductor-based photocatalyst (tungsten, titania, zinc, etc.), structure modification of photocatalyst (doping, heterojunction, surface modification, crystal facet re-arrangement, and electron scavenger), factors affecting the reaction process (physiochemical characteristic of photocatalyst, operational condition, and reactor configuration), and briefly proposed reaction mechanism. Analysis of existing challenges and recommendations for the future development of photocatalytic technology for methane to methanol conversion is also highlighted.


Introduction
Energy plays a vital role in ensuring national security. It becomes a concern because the demand is growing rapidly along with economic development, population growth, and technological development. Currently, energy resources rely on non-renewable energy, such as fossil fuels (coal, natural gas, and oil). Meanwhile, the availability of these resources is finite and will be vanished if they continue to be exploited unwisely. On the other hand, fossil fuel combustion produces CO 2 that will exacerbate global warming.
The global warming issue has attracted a lot of attention. Through the 2015 Paris Agreement, many countries have committed to contributing to climate change mitigation and reducing greenhouse gas emissions. According to Environmental Protection Agency (EPA), methane is the second-largest contributor to climate change accounting for about Methane is the simplest hydrocarbon with a symmetric tetrahedral structure leading methane to have low polarizability and low electron and proton affinity [2]. Methane is a very stable and non-reactive substance. Therefore, it is difficult to activate the C-H bond; hence, high pressure and temperature are required. As the main component of natural gas, methane has a high caloric value and is classified as a good hydrogen source. It is converted into various chemicals such as syngas for ammonia production, methanol, hydrocarbon, acetylene, and carbon disulfide. It can also be used directly as fuel by direct combustion (Figure 2).  [3]. Reproduced with permission from Holmen. Copyright © 2022 Elsevier. Methanol and ammonia are the most critical methane conversion products required in large quantities [3]. Liquefaction of methane to methanol is preferred over gaseous Methane is the simplest hydrocarbon with a symmetric tetrahedral structure leading methane to have low polarizability and low electron and proton affinity [2]. Methane is a very stable and non-reactive substance. Therefore, it is difficult to activate the C-H bond; hence, high pressure and temperature are required. As the main component of natural gas, methane has a high caloric value and is classified as a good hydrogen source. It is converted into various chemicals such as syngas for ammonia production, methanol, hydrocarbon, acetylene, and carbon disulfide. It can also be used directly as fuel by direct combustion (Figure 2). and reducing greenhouse gas emissions. According to Environmental Protection Agency (EPA), methane is the second-largest contributor to climate change accounting for about 10% of all greenhouse gasses emitted in 2019. The Intergovernmental Panel on Climate Change (IPCC) states that comparatively, it has 34 times greater Global Warming Potential (GWP) than carbon dioxide ( Figure 1). Methane is emitted from natural sources (wetlands, termites, marine, freshwater, and CH4 hydrate) and human activities (energy, industry, agriculture, land use, and waste management). Globally, 50-65 percent of total methane in the atmosphere emits from human activities. Methane is the simplest hydrocarbon with a symmetric tetrahedral structure leading methane to have low polarizability and low electron and proton affinity [2]. Methane is a very stable and non-reactive substance. Therefore, it is difficult to activate the C-H bond; hence, high pressure and temperature are required. As the main component of natural gas, methane has a high caloric value and is classified as a good hydrogen source. It is converted into various chemicals such as syngas for ammonia production, methanol, hydrocarbon, acetylene, and carbon disulfide. It can also be used directly as fuel by direct combustion (Figure 2). Methanol can be produced by selective oxidation through indirect or direct methods [5]. Industrially, indirect methods are employed for the production of methanol. The process produces intermediate syngas (CO and H 2 ) through steam or dry reforming, then hydrogenated to obtain methanol. However, the syngas process is highly endothermic, requiring a large external energy supply. Therefore, this process still has many drawbacks, such as high energy consumption, complicated operation, catalyst deactivation, and reactor stability [6,7]. The direct method of methanol production is desirable to reduce production costs because the process bypasses syngas production. However, the target product is still unsatisfactory due to the low selectivity of methanol.
Zakaria and Kamarudin [8] have summarized several relevant technologies to convert methane into methanol. These include conventional catalytic processes, plasma technology, supercritical water, biological (membrane), and photocatalytic technology. However, some drawbacks are still inevitable, including (i) the relatively slow selectivity of methanol formation for conventional catalytic technology; (ii) low conversion productivity and limited by the amount of methane that can be dissolved in water for plasma technology; (iii) reactor design and high corrosion rate when treating effluents containing halogen for supercritical water processes; (iv) membrane incompatibility due to methane permeability, which can cause dissolution, swelling, or breakage of the membrane; and (v) limitations of investigation of photocatalysts and suitable photoreactors for photocatalytic technology [8].
It is desirable to synthesize methane at a lower temperature to reduce energy consumption and maintain catalyst stability. Among several technologies, photocatalytic technology seems to be a promising method for the conversion of methane conversion to methanol, as it offers an effective way to produce methanol using renewable solar energy under ambient conditions. Furthermore, photon energy that exceeds activation energy for a specific chemical reaction promotes the redox reaction. Therefore, the involvement of solar energy to facilitate photocatalytic reaction exhibits more environmentally friendly, sustainable, and renewable than fossil fuel-based energy. This technology can also reduce production costs and increase economic benefits. In addition, catalyst deactivation will be significantly reduced due to the low temperature and pressure used (under ambient conditions) in the photocatalytic process. Figure 4 shows the number of publications on the utilization of photocatalytic technology in general and specifically for converting methane to methanol from 2000 to 2020. The increasing number of scientific publications on photocatalytic technology for methane to methanol conversion provides clear evidence that this topic is significant. In addition, many researchers studied the effect of different structure engineering and nanomaterials on the performance of photocatalysts since their energy conversion efficiency is principally Figure 4 shows the number of publications on the utilization of photocatalytic technology in general and specifically for converting methane to methanol from 2000 to 2020. The increasing number of scientific publications on photocatalytic technology for methane to methanol conversion provides clear evidence that this topic is significant. In addition, many researchers studied the effect of different structure engineering and nanomaterials on the performance of photocatalysts since their energy conversion efficiency is principally influenced by the physicochemical properties of photocatalysts and operating conditions during the photocatalytic reaction. This paper will systematically review and discuss recent advances in photocatalytic methane oxidation to methanol ( Figure 5). The scope of this review consists of the fundamentals of the photocatalytic process, particularly methane oxidation to methanol, the development of photocatalysts and their modification to achieve optimum conversion efficiency, and factors affecting the efficiency of photocatalysts to facilitate methane oxidation to methanol. Hopefully, this review will help researchers understand the fundamental photocatalytic reaction process of methane conversion to methanol in-depth and ultimately provide inspiration for developing novel composite materials based on the existing state-of-the-art photocatalysts.  This paper will systematically review and discuss recent advances in photocatalytic methane oxidation to methanol ( Figure 5). The scope of this review consists of the fundamentals of the photocatalytic process, particularly methane oxidation to methanol, the development of photocatalysts and their modification to achieve optimum conversion efficiency, and factors affecting the efficiency of photocatalysts to facilitate methane oxidation to methanol. Hopefully, this review will help researchers understand the fundamental photocatalytic reaction process of methane conversion to methanol in-depth and ultimately provide inspiration for developing novel composite materials based on the existing stateof-the-art photocatalysts.

Heterogeneous Photocatalyst for Photo-Oxidation Methane to Methanol
Photocatalysis is commonly referred to as artificial photosynthesis since the photosynthetic system inspires the process. The essence of natural photosynthesis is to drive chemical reactions using optical photon energy. Upon illumination of sunlight, oxygen

Heterogeneous Photocatalyst for Photo-Oxidation Methane to Methanol
Photocatalysis is commonly referred to as artificial photosynthesis since the photosynthetic system inspires the process. The essence of natural photosynthesis is to drive chemical reactions using optical photon energy. Upon illumination of sunlight, oxygen (O 2 ) is produced from the oxidation of water (H 2 O) and carbon dioxide (CO 2 ), which further transform to generate hydrocarbons with the help of chlorophylls to absorb and transfer photon energy [9]. The broad definition of photocatalysis can also be adopted from IUPAC, which can be defined as a "Change in the rate of a chemical reaction or its initiation under the action of ultraviolet, visible or infrared radiation in the presence of a substance-the photocatalyst-that absorbs light and is involved in the chemical transformation of the reaction partners." Currently, photocatalytic technology has been widely applied to solve problems related to air pollution [10] and environmental remediation of water contaminants [11], including dyes degradation [12], organic pollutants removal [13][14][15], heavy metals removal [16], and oil degradation in wastewater [17]. In addition, photocatalytic technology provides alternative ways to produce renewable energy, including water splitting, CO 2 reduction, N 2 fixation, and, in particular, CH 4 oxidation to methanol [9].

Thermodynamics for Methane to Methanol Conversion
Methane has very stable and strong C-H bonds in the CH 4 molecules, which remain challenging to convert methane into more useful hydrocarbon and hydrogen. Table 1 shows the change in Gibbs free energy for various methane reactions in 298 K (∆G 98 ). Most of the reactions have a positive ∆G 298 indicating that the reaction is unfavorable and cannot proceed spontaneously without adding external energy as a driving force. Total oxidation Oxidative coupling of methane (OCM) Partial oxidation of methane (POM) Methane to methanol Steam reforming of methane (SRM) Water-gas shift reaction SRM + water-gas shift reaction 114 13 Methane to acetic acid Methane to amino acids Methanol from methane in the industry is produced indirectly from a steam reforming process using a nickel-based catalyst followed by high-pressure catalytic conversion of the synthetic gas to methanol ( Figure 6). Steam reforming is an unfavorable thermodynamic reaction and can only be proceeded at high temperature and pressure ( Table 1, No. 10). Nevertheless, this process can produce H 2 with high purity. However, there are still challenges, such as high energy consumption due to the formation of highly endothermic syngas [5], low catalyst activity, which still needs further development [19], and complex treatment to prevent heat transfer problems [19].
ing process using a nickel-based catalyst followed by high-pressure catalytic conversion of the synthetic gas to methanol ( Figure 6). Steam reforming is an unfavorable thermodynamic reaction and can only be proceeded at high temperature and pressure ( Table 1, No. 10). Nevertheless, this process can produce H2 with high purity. However, there are still challenges, such as high energy consumption due to the formation of highly endothermic syngas [5], low catalyst activity, which still needs further development [19], and complex treatment to prevent heat transfer problems [19]. Methanol can also be obtained from the direct conversion of methane with water ( Table 1, No. 9). Thermodynamically, converting methane into methanol using water as a Methanol can also be obtained from the direct conversion of methane with water ( Table 1, No. 9). Thermodynamically, converting methane into methanol using water as a reactant is an endothermic process (∆H 0 298 = 77 kJ/mol). However, this process is thermodynamically unfavorable at any temperature, as reflected by the Gibbs free energy data at a temperature range of 273 K to 1500 K (Table 2). Furthermore, photocatalytic reaction offers an alternative way to facilitate these unfavorable reactions under ambient conditions. The process includes methane and water as the reactant and light as the driving force.

Proposed Mechanism of Photocatalytic Conversion of Methane to Methanol
The development of the conversion of methane to methanol by photocatalytic technology was initiated by Ogura & Kataoka [20]. The reaction involves water vapor at temperatures below 100 • C, methane gas, and UV irradiation at atmospheric pressure. First, methane gas continuously flowed into the water surface to obtain a mixture of water vapor and methane. Then, the mixture of water vapor and methane reacted and produced methanol as the main product. The brief mechanism of photochemical methane conversion in the research conducted by Ogura and Kataoka [20] is shown in Equations (1)- (4).
The reaction begins with the photolysis of water to produce a hydroxyl radical (•OH). The hydroxyl radical then reacts with methane to produce methyl radicals (•CH 3 ). Finally, the methyl radical reacts with other water molecules to produce methanol and hydrogen. Furthermore, Noceti et al. [21] combined two reactions, including water splitting and methane conversion, to produce methanol and hydrogen using La/WO 2 -based photocatalyst, as shown briefly in Equations (5)- (10). The reaction was carried out at a temperature of 94 • C, atmospheric pressure, and with visible light irradiation has succeeded in oxidizing However, the first obstacle in the photocatalytic conversion of methane to methanol is how to activate the highly stable methane molecule. There are two possible scenarios for activating methane using a semiconductor-based catalyst [22].  Figure 7. This reaction depends on the reaction of the applied system, such as the type of semiconductor and any other additional substance added. •CH3 + H2O ⟶ CH3OH + ½ H2 (10) However, the first obstacle in the photocatalytic conversion of methane to methanol is how to activate the highly stable methane molecule. There are two possible scenarios for activating methane using a semiconductor-based catalyst [22]. Methane can be activated directly by photogenerated holes in the VB where •OH is produced by reduction of H2O2 and oxidation of H2O while •O2 − produced during the reaction by H2O2 and •OH. Methanol can be obtained by: (i) reaction of methyl radical (•CH3) with •OH, (ii) reaction of •OCH3 with H2O, or (iii) reduction of CH3OOH generated by the integration of •CH3 and O2. Methane can also be activated indirectly by any active oxygenated radical species, as illustrated in Figure 7. This reaction depends on the reaction of the applied system, such as the type of semiconductor and any other additional substance added. Gondal et al. [23] proposed a mechanism for methane activation through •OH produced by the photocatalytic process. Several studies have adopted this mechanism, as illustrated in Figure 8a [24,25]. Xie et al. [26] proposed a typical reaction of photocatalytic methanol production from methane with simultaneous production of •OH by reduction of H2O2 and •CH3 by oxidation of methane in the VB by the photogenerated hole. Methanol is obtained through the reaction between •CH3 and •OH, which probably occurs in iron species as a dopant. Zeng et al. [27] proposed a mechanism for converting methane to methanol with the addition of iron ions and H2O2 species called photocatalysis of the Fenton reaction (PCFR) (Figure 8b). The schematic mechanism for selective conversion of methane to methanol can also be achieved, as illustrated in Figure 8c. Zhou [28] proposed a methane activation mechanism by reducing O2 in the conduction band and oxidation of H2O in the valence band. Methanol will be produced by a direct combination of •CH3 and •OH and reduction of CH3OOH generated by the integration of •CH3 and O2 (Figure 8d). Moreover, the role of each active species, including e − , •O2 − , •OH, and h + was studied by utilizing K2Cr2O7, para-quinone, salicylic acid and Na2C2O4 as scavengers to trap those active species formed in the PCFR process, respectively ( Figure 9). Based on these findings, e − played the most dominant role in methanol production, followed by •O2 − , •OH, and h + . Gondal et al. [23] proposed a mechanism for methane activation through •OH produced by the photocatalytic process. Several studies have adopted this mechanism, as illustrated in Figure 8a [24,25]. Xie et al. [26] proposed a typical reaction of photocatalytic methanol production from methane with simultaneous production of •OH by reduction of H 2 O 2 and •CH 3 by oxidation of methane in the VB by the photogenerated hole. Methanol is obtained through the reaction between •CH 3 and •OH, which probably occurs in iron species as a dopant. Zeng et al. [27] proposed a mechanism for converting methane to methanol with the addition of iron ions and H 2 O 2 species called photocatalysis of the Fenton reaction (PCFR) (Figure 8b). The schematic mechanism for selective conversion of methane to methanol can also be achieved, as illustrated in Figure 8c. Zhou [28] proposed a methane activation mechanism by reducing O 2 in the conduction band and oxidation of H 2 O in the valence band. Methanol will be produced by a direct combination of •CH 3 and •OH and reduction of CH 3 OOH generated by the integration of •CH 3 and O 2 ( Figure 8d). Moreover, the role of each active species, including e − , •O 2 − , •OH, and h + was studied by utilizing K 2 Cr 2 O 7 , para-quinone, salicylic acid and Na 2 C 2 O 4 as scavengers to trap those active species formed in the PCFR process, respectively ( Figure 9). Based on these findings, e − played the most dominant role in methanol production, followed by •O 2 − , •OH, and h + .
Based on several studies, it is found that the hydroxyl radical plays a crucial role in the photocatalytic conversion of methane to methanol. This species can be obtained either by photooxidation of H2O or photoreduction of H2O2. In general, H2O2 is added to facilitate the formation of •OH and, thus, enhance photocatalytic efficiency. For example, Noceti et al. [21] reported that adding H2O2 to the reaction carried out at atmospheric pressure, and temperature of 94 °C with irradiation from a mercury lamp (46% visible light) increased methane conversion from 4% to 10%, accompanied by increased CO2 Figure 8. Several proposed schematic mechanisms for selective conversion of methane to methanol were reported by (a) Negishi et al. [25], (b) Xie et al. [26], (c) Zeng et al. [27], and (d) Zhou et al. [28]. Reproduced with permission from Negishi Based on several studies, it is found that the hydroxyl radical plays a crucial role in the photocatalytic conversion of methane to methanol. This species can be obtained either by photooxidation of H2O or photoreduction of H2O2. In general, H2O2 is added to facilitate the formation of •OH and, thus, enhance photocatalytic efficiency. For example, Noceti et al. [21] reported that adding H2O2 to the reaction carried out at atmospheric pressure, and temperature of 94 °C with irradiation from a mercury lamp (46% visible light) increased methane conversion from 4% to 10%, accompanied by increased CO2 Based on several studies, it is found that the hydroxyl radical plays a crucial role in the photocatalytic conversion of methane to methanol. This species can be obtained either by photooxidation of H 2 O or photoreduction of H 2 O 2 . In general, H 2 O 2 is added to facilitate the formation of •OH and, thus, enhance photocatalytic efficiency. For example, Noceti et al. [21] reported that adding H 2 O 2 to the reaction carried out at atmospheric pressure, and temperature of 94 • C with irradiation from a mercury lamp (46% visible light) increased methane conversion from 4% to 10%, accompanied by increased CO 2 formation. Zeng et al. [27] also reported excellent results in reactions using TiO 2 photocatalyst and addition of H 2 O 2 under visible light irradiation, with methanol yields up to 850 mol g −1 h −1 and a selectivity of 83%.
On the other hand, a study conducted by Gondal et al. [29] showed the opposite effect, where the addition of H 2 O 2 exhibited a lower yield of methanol than the reaction without H 2 O 2 addition using WO 3 photocatalyst under visible laser irradiation and ambient conditions. These results are believed to be due to the usage of a visible laser lamp providing higher photon flux density monochromatic light than the conventional lamp so that more •OH was formed. These •OH radicals are also a major source of O 2 that facilitates further oxidation of methanol. These results agree with Villa et al. [30], which carried out a reaction using WO 3 photocatalyst at atmospheric pressure, the temperature of 55 • C, and under UVC-Vis irradiation. It was found that the formation of ethane accompanied the methanol production due to the higher amount of •OH activated methane to generate more •CH 3 , as shown in Equation (11).
•CH 3 + •CH 3 → C 2 H 6 (11) Based on these findings, Villa et al. [24] proposed a strategy to incorporate fluorine on the WO 3 photocatalyst surface to minimize the interaction between the catalyst and the reactants. The schematic reaction mechanism on the surface of the WO 3 before and after the incorporation of fluorine is shown in Figure 10. It was found that •OH groups on the catalyst surface are mainly responsible for enhancing the performance of WO 3 in the selective oxidation of methane to methanol. At the same time, an enormous amount of free OH radicals favor the formation of ethane. Therefore, adding a hydroxyl radical generator, i.e., H 2 O 2 , can increase methane conversion [31]. However, such an appropriate amount of H 2 O 2 is essential for controlling the selectivity of methanol [22,23,27]. formation. Zeng et al. [27] also reported excellent results in reactions using TiO2 photocatalyst and addition of H2O2 under visible light irradiation, with methanol yields up to 850 mol g −1 h −1 and a selectivity of 83%. On the other hand, a study conducted by Gondal et al. [29] showed the opposite effect, where the addition of H2O2 exhibited a lower yield of methanol than the reaction without H2O2 addition using WO3 photocatalyst under visible laser irradiation and ambient conditions. These results are believed to be due to the usage of a visible laser lamp providing higher photon flux density monochromatic light than the conventional lamp so that more •OH was formed. These •OH radicals are also a major source of O2 that facilitates further oxidation of methanol. These results agree with Villa et al. [30], which carried out a reaction using WO3 photocatalyst at atmospheric pressure, the temperature of 55 °C, and under UVC-Vis irradiation. It was found that the formation of ethane accompanied the methanol production due to the higher amount of •OH activated methane to generate more •CH3, as shown in Equation (11).
Based on these findings, Villa et al. [24] proposed a strategy to incorporate fluorine on the WO3 photocatalyst surface to minimize the interaction between the catalyst and the reactants. The schematic reaction mechanism on the surface of the WO3 before and after the incorporation of fluorine is shown in Figure 10. It was found that •OH groups on the catalyst surface are mainly responsible for enhancing the performance of WO3 in the selective oxidation of methane to methanol. At the same time, an enormous amount of free OH radicals favor the formation of ethane. Therefore, adding a hydroxyl radical generator, i.e., H2O2, can increase methane conversion [31]. However, such an appropriate amount of H2O2 is essential for controlling the selectivity of methanol [22,23,27]. Methanol, the primary desired main product of methane oxidation, is more reactive than methane itself. Thus, methanol can be easily oxidized further when some of the following conditions occur, such as: 1. The formation of superoxide radicals (•O2 − ) produced via the reduction of O2 in CB of semiconductor [23], shown in Equations (12)- (14). Methanol, the primary desired main product of methane oxidation, is more reactive than methane itself. Thus, methanol can be easily oxidized further when some of the following conditions occur, such as: 1.

2.
A sufficient amount of methanol generation either competes with water to further react with a photogenerated hole in VB or direct interaction with •OH to produce side products such as formaldehyde [32], as shown in Equations (15) According to the abovementioned issues, it is essential to control the oxidative power of the system to achieve optimum methanol selectivity. For instance, using a moderate photocatalyst lowers the potential reduction of H 2 O 2 [26] and prevents O 2 reduction to form •O 2 − by adding an electron scavengers agent [29]. In addition, the yield of methanol can be enhanced by continuous removal of the methanol after its formation to prevent further oxidation of methanol [32].

Selection of Materials for Photocatalytic Methane to Methanol Conversion
Heterogeneous photocatalysts have been widely studied and applied to photocatalytic processes. This catalyst only requires energy from photons to drive the reaction under ambient conditions, unlike conventional catalysts that require heat or high-temperature conditions. Upon illumination of light with sufficient energy (higher or equal to band gap energy of semiconductor-based photocatalysts), the photon energy from the light is absorbed by the semiconductor and initiates the excitation of electron (e − ) from VB to CB, leaving a hole (h + ) in VB. Photogenerated electron-hole or charged pairs are responsible for promoting redox reactions on the photocatalyst surface.
The ideal semiconductor photocatalyst must be chemically and biologically inert, photo-catalytically stable, easy to manufacture and use, can be activated by low energy of light, i.e., sunlight, catalyze reactions efficiently, inexpensive, and environmentally friendly [33]. The crucial semiconductor properties required to establish a successful chemical photoreaction include band gap energy, energy band position of the semiconductor, and the appropriate redox potential of the adsorbate to produce the desired product. Thus, it is fundamental to identify the Highest Occupied Molecular Orbital (HOMO) and Lowest Unoccupied Molecular Orbital (LUMO) of the semiconductors involved in the charge transfer during the reaction. HOMO coincides with the top of the VB, where all electronic levels are occupied, while LUMO coincides with the bottom of CB, where all electronic levels are empty [34].
Based on the appropriate redox potential, several semiconductors have the potential to carry out the photocatalytic conversion of methane to methanol, such as TiO 2 , WO 3 , BiVO 4 , ZnO, Fe 2 O 3 , NiO, and CuO ( Figure 11). Those semiconductors have an absolute energy position of the VB below the potential oxidation of H 2 O/•OH to allow hole transfer to the reactant to carry out the oxidation reaction and also an absolute energy position of CB above the potential reduction of O 2 /•O 2 − and H 2 O 2 /•OH to allow the donation of the excited electron to carry out the reduction reaction.
Heterogeneous photocatalysts can be obtained from pure/basic metal oxide or modified metal oxide. The intrinsic properties of metal oxide, such as a range of light absorption, electronic band structure, specific surface area, particle size, and morphology, are considered for its application as a photocatalyst. Generally, getting a pure metal oxide with high applicability is challenging to fulfill all photocatalytic reaction prerequisites. Therefore, it is necessary to modify the semiconductor to adjust and improve their properties toward defined requirements for their intended use. Common metal oxides and their modification, including their properties, photocatalytic activity and their drawbacks toward methanol production, will be discussed in the below section. Heterogeneous photocatalysts can be obtained from pure/basic metal oxide or m ified metal oxide. The intrinsic properties of metal oxide, such as a range of light abs tion, electronic band structure, specific surface area, particle size, and morphology considered for its application as a photocatalyst. Generally, getting a pure metal o with high applicability is challenging to fulfill all photocatalytic reaction prerequi Therefore, it is necessary to modify the semiconductor to adjust and improve their p erties toward defined requirements for their intended use. Common metal oxides their modification, including their properties, photocatalytic activity and their drawb toward methanol production, will be discussed in the below section.

Pure Semiconductor
Due to their unique electronic properties, semiconductors have been widely use photocatalyst material in photocatalytic reactions. Therefore, the performance of diffe pure semiconductors is studied and compared in the same reaction condition or with pure semiconductors. Among various semiconductors, tungsten, titanium, bismuth, and iron-based semiconductor are the most frequently studied for photocatalytic ox tion of methane to methanol since they show promising activity. Therefore, this sec will review each pure semiconductor's performance toward methane photo-oxidatio methanol.
Tungsten-based semiconductors are commonly found as photocatalysts in the of WO3. It is one of the most common semiconductors used as a photocatalyst for met oxidation to methanol due to its unique chemical, functional, and physical properties cost, small band gap energy (2.4-2.8 eV), and stable physicochemical properties [36 addition, it has moderate oxidizing power, preferable for methanol production from thane oxidation [37]. WO3 was also demonstrated to effectively absorb visible light, w is the most energy in sunlight. However, pure WO3 is still difficult to apply since confronted with the rapid recombination of photogenerated electron-hole pairs [36]. T modification of WO3 to prevent the recombination losses of charge carriers is neces and crucial.
Titanium dioxide (TiO2) is the most widely used semiconductor for photocatalyst to its wide band gap, lower price, high photocatalytic activity, considerable photostab non-toxicity, ample availability, insolubility in aqueous solution, and chemical and logical inertness [38]. Currently, TiO2 materials are used for many applications, inclu water splitting [39], water treatment [40], air pollution treatment [10], solar cells [41], many other applications ( Figure 12).

Pure Semiconductor
Due to their unique electronic properties, semiconductors have been widely used as photocatalyst material in photocatalytic reactions. Therefore, the performance of different pure semiconductors is studied and compared in the same reaction condition or with impure semiconductors. Among various semiconductors, tungsten, titanium, bismuth, zinc, and iron-based semiconductor are the most frequently studied for photocatalytic oxidation of methane to methanol since they show promising activity. Therefore, this section will review each pure semiconductor's performance toward methane photo-oxidation to methanol.
Tungsten-based semiconductors are commonly found as photocatalysts in the form of WO 3 . It is one of the most common semiconductors used as a photocatalyst for methane oxidation to methanol due to its unique chemical, functional, and physical properties, low cost, small band gap energy (2.4-2.8 eV), and stable physicochemical properties [36]. In addition, it has moderate oxidizing power, preferable for methanol production from methane oxidation [37]. WO 3 was also demonstrated to effectively absorb visible light, which is the most energy in sunlight. However, pure WO 3 is still difficult to apply since it is confronted with the rapid recombination of photogenerated electron-hole pairs [36]. Thus, modification of WO 3 to prevent the recombination losses of charge carriers is necessary and crucial.
Titanium dioxide (TiO 2 ) is the most widely used semiconductor for photocatalyst due to its wide band gap, lower price, high photocatalytic activity, considerable photostability, non-toxicity, ample availability, insolubility in aqueous solution, and chemical and biological inertness [38]. Currently, TiO 2 materials are used for many applications, including water splitting [39], water treatment [40], air pollution treatment [10], solar cells [41], and many other applications ( Figure 12). The crystal structure of TiO2 can be classified into three phases: anatase, rutile, and brookite ( Figure 13), where each has different characteristics and band gaps. Anatase is stable at low temperature and has a band gap of 3.2 eV, while rutile is stable at high temperature and has a band gap of 3.0 eV. Meanwhile, brookite is usually found in minerals with orthorhombic crystal structure and has a band gap of 3.25 eV [38,43,44]. Anatase has the highest photocatalytic activity among other TiO2 crystal phases because it has the lightest average effective mass of photogenerated electrons, a higher surface adsorption capacity to hydroxyl groups, and a lower charge carrier recombination rate than rutile and photoexcited charge carriers are more easily to migrate and transfer to the surface [45,46]. In addition, anatase TiO2 has a wide band gap which puts this semiconductor as a UV light-absorbing semiconductor. Therefore, it displays a high photocatalytic activity when irradiated by UV light. However, it remains a challenge that needs to resolve for semiconductor TiO2 because it is desired for a photocatalytic process to absorb visible light wavelength. The bismuth-based semiconductor is a visible-light responsive photocatalyst that provides an excellent opportunity to convert sunlight into chemical energy. Every bismuth-based material usually possesses narrow band gaps less than 3.0 eV due to their electronic structure in the valence band, which consists of oxygen 2p and bismuth 6s [47]. In the photocatalytic process, bismuth-based material can be prepared as Bi2O3, Bi2MO6 The crystal structure of TiO 2 can be classified into three phases: anatase, rutile, and brookite ( Figure 13), where each has different characteristics and band gaps. Anatase is stable at low temperature and has a band gap of 3.2 eV, while rutile is stable at high temperature and has a band gap of 3.0 eV. Meanwhile, brookite is usually found in minerals with orthorhombic crystal structure and has a band gap of 3.25 eV [38,43,44]. Anatase has the highest photocatalytic activity among other TiO 2 crystal phases because it has the lightest average effective mass of photogenerated electrons, a higher surface adsorption capacity to hydroxyl groups, and a lower charge carrier recombination rate than rutile and photoexcited charge carriers are more easily to migrate and transfer to the surface [45,46]. In addition, anatase TiO 2 has a wide band gap which puts this semiconductor as a UV light-absorbing semiconductor. Therefore, it displays a high photocatalytic activity when irradiated by UV light. However, it remains a challenge that needs to resolve for semiconductor TiO 2 because it is desired for a photocatalytic process to absorb visible light wavelength. The crystal structure of TiO2 can be classified into three phases: anatase, rutile, and brookite ( Figure 13), where each has different characteristics and band gaps. Anatase is stable at low temperature and has a band gap of 3.2 eV, while rutile is stable at high temperature and has a band gap of 3.0 eV. Meanwhile, brookite is usually found in minerals with orthorhombic crystal structure and has a band gap of 3.25 eV [38,43,44]. Anatase has the highest photocatalytic activity among other TiO2 crystal phases because it has the lightest average effective mass of photogenerated electrons, a higher surface adsorption capacity to hydroxyl groups, and a lower charge carrier recombination rate than rutile and photoexcited charge carriers are more easily to migrate and transfer to the surface [45,46]. In addition, anatase TiO2 has a wide band gap which puts this semiconductor as a UV light-absorbing semiconductor. Therefore, it displays a high photocatalytic activity when irradiated by UV light. However, it remains a challenge that needs to resolve for semiconductor TiO2 because it is desired for a photocatalytic process to absorb visible light wavelength. The bismuth-based semiconductor is a visible-light responsive photocatalyst that provides an excellent opportunity to convert sunlight into chemical energy. Every bismuth-based material usually possesses narrow band gaps less than 3.0 eV due to their electronic structure in the valence band, which consists of oxygen 2p and bismuth 6s [47]. In the photocatalytic process, bismuth-based material can be prepared as Bi2O3, Bi2MO6 The bismuth-based semiconductor is a visible-light responsive photocatalyst that provides an excellent opportunity to convert sunlight into chemical energy. Every bismuthbased material usually possesses narrow band gaps less than 3.0 eV due to their electronic structure in the valence band, which consists of oxygen 2p and bismuth 6s [47]. In the photocatalytic process, bismuth-based material can be prepared as Bi 2 O 3 , Bi 2 MO 6 (M = Cr, Mo, and W), BiVO 4 , BiOX (X = Cl, Br and I), BiPO 4 , (BiO) 2 CO 3 , and pentavalent bismuthates [44]. Bismuth-based semiconductors are widely used as photocatalysts for many applications such as water splitting [48], pollutant degradation [14], CO 2 reduction/N 2 fixation [49], and organic synthesis ( Figure 14). (M = Cr, Mo, and W), BiVO4, BiOX (X = Cl, Br and I), BiPO4, (BiO)2CO3, and pentavalent bismuthates [44]. Bismuth-based semiconductors are widely used as photocatalysts for many applications such as water splitting [48], pollutant degradation [14], CO2 reduction/N2 fixation [49], and organic synthesis ( Figure 14). Zinc-based photocatalyst is commonly used as a photocatalyst in the form of zinc oxide (ZnO). ZnO has a broad direct band gap (3.37 eV) which corresponds to ultraviolet absorption and large excitation binding energy (60 meV) [51,52]. As a result, it shows excellent electrical, mechanical, and optical properties, similar to TiO2 [53]. Besides that, it possesses a lower production cost of photocatalyst [54] and higher absorption efficiency across a more significant fraction of the solar spectrum than TiO2 [51]. The ZnO semiconductor is generally studied in photocatalytic reactions for dye degradation coupling with various kinds of dopants, such as transition metal [55], alkaline earth [56], a nonmetal [57], zeolite [58], rare metal-earth [59], and other metals [60]. However, the study of ZnO for photocatalyst toward photocatalytic oxidation methane to methanol is still limited compared with WO3 and TiO2. Moreover, the ZnO photocatalyst application encounters some constraints, such as its limited light-harvesting ability, photo-corrosion severe problem, and rapid recombination of electron-hole pairs [61].
Iron oxides exist in many forms in nature, such as magnetite (Fe3O4), hematite (α-Fe2O3), and maghemite (γ-Fe2O3) [11]. It has low cost, high stability, and compatibility with the value of the direct and indirect band gap nanomaterials ranging from 1.95 to 2.35 eV and 1.38 to 2.09 eV, respectively [62]. This semiconductor has been widely applied for wastewater treatment [63,64]. However, the iron-based photocatalyst is hardly ever found as the primary catalyst used in the photocatalytic oxidation of methane to methanol. Commonly, it is used as a dopant, cocatalyst, and electron scavenger in the reaction system and noticeably shows a remarkable improvement in the reaction.
The performance of those metal oxide semiconductors has been studied in the form of their pure/bare metal oxide in the photocatalytic oxidation of methane to methanol. For example, Gondal [23] studied the performance of several pure semiconductors (WO3, TiO2, and NiO) in the same reaction condition. Photocatalyst WO3 exhibited the highest methane conversion with the conversion of WO3, TiO2, and NiO, 29%, 21%, and 20%, respectively. On the other hand, Xie [26] studied the pure anatase of TiO2 compared with iron-doped-TiO2. The reaction was conducted over 3 h of irradiation and showed a methane conversion rate of 10.9%, but lower methanol selectivity of 36% compared with irondoped-TiO2. Zinc-based photocatalyst is commonly used as a photocatalyst in the form of zinc oxide (ZnO). ZnO has a broad direct band gap (3.37 eV) which corresponds to ultraviolet absorption and large excitation binding energy (60 meV) [51,52]. As a result, it shows excellent electrical, mechanical, and optical properties, similar to TiO 2 [53]. Besides that, it possesses a lower production cost of photocatalyst [54] and higher absorption efficiency across a more significant fraction of the solar spectrum than TiO 2 [51]. The ZnO semiconductor is generally studied in photocatalytic reactions for dye degradation coupling with various kinds of dopants, such as transition metal [55], alkaline earth [56], a nonmetal [57], zeolite [58], rare metal-earth [59], and other metals [60]. However, the study of ZnO for photocatalyst toward photocatalytic oxidation methane to methanol is still limited compared with WO 3 and TiO 2 . Moreover, the ZnO photocatalyst application encounters some constraints, such as its limited light-harvesting ability, photo-corrosion severe problem, and rapid recombination of electron-hole pairs [61].
Iron oxides exist in many forms in nature, such as magnetite (Fe 3 O 4 ), hematite (α-Fe 2 O 3 ), and maghemite (γ-Fe 2 O 3 ) [11]. It has low cost, high stability, and compatibility with the value of the direct and indirect band gap nanomaterials ranging from 1.95 to 2.35 eV and 1.38 to 2.09 eV, respectively [62]. This semiconductor has been widely applied for wastewater treatment [63,64]. However, the iron-based photocatalyst is hardly ever found as the primary catalyst used in the photocatalytic oxidation of methane to methanol. Commonly, it is used as a dopant, cocatalyst, and electron scavenger in the reaction system and noticeably shows a remarkable improvement in the reaction.
The performance of those metal oxide semiconductors has been studied in the form of their pure/bare metal oxide in the photocatalytic oxidation of methane to methanol. For example, Gondal [23] studied the performance of several pure semiconductors (WO 3 , TiO 2 , and NiO) in the same reaction condition. Photocatalyst WO 3 exhibited the highest methane conversion with the conversion of WO 3 , TiO 2 , and NiO, 29%, 21%, and 20%, respectively. On the other hand, Xie [26] studied the pure anatase of TiO 2 compared with iron-doped-TiO 2 . The reaction was conducted over 3 h of irradiation and showed a methane conversion rate of 10.9%, but lower methanol selectivity of 36% compared with iron-doped-TiO 2 .
Lopez [65] evaluated several synthesized bismuth-based materials in the selective photooxidation of methane. The reaction was performed in a photochemical reactor equipped with an immersion medium-pressure mercury lamp (450 W) at 55 • C for 120 min of irradiation, with CH 3 OH, CO 2 , and C 2 H 6 as the main products. BiVO 4 showed better methanol selectivity and lower CO 2 and C 2 H 6 levels ( Figure 15). Moreover, it also showed a minimal change of color in contrast with BiWO 6 , which showed a shift in color suspension at the end of the test.
A study by Zeng [27] reported using Fe 2 O 3 as a photocatalyst in the conversion of methane to methanol and showed a lower methane conversion and methanol selectivity than TiO 2 photocatalyst. Song [66] studied pure ZnO and TiO 2 catalyst compared with the doped photocatalyst. The reaction was conducted in a 230 mL batch-reactor equipped with a quartz window, 2 MPa pressurized methane, and under a 300 W Xenon lamp. Methanol was not produced in both photocatalysts, while CO and CO 2 were detected with higher production in TiO 2 . Lopez [65] evaluated several synthesized bismuth-based materials in the selective photooxidation of methane. The reaction was performed in a photochemical reactor equipped with an immersion medium-pressure mercury lamp (450 W) at 55 °C for 120 min of irradiation, with CH3OH, CO2, and C2H6 as the main products. BiVO4 showed better methanol selectivity and lower CO2 and C2H6 levels ( Figure 15). Moreover, it also showed a minimal change of color in contrast with BiWO6, which showed a shift in color suspension at the end of the test. A study by Zeng [27] reported using Fe2O3 as a photocatalyst in the conversion of methane to methanol and showed a lower methane conversion and methanol selectivity than TiO2 photocatalyst. Song [66] studied pure ZnO and TiO2 catalyst compared with the doped photocatalyst. The reaction was conducted in a 230 mL batch-reactor equipped with a quartz window, 2 MPa pressurized methane, and under a 300 W Xenon lamp. Methanol was not produced in both photocatalysts, while CO and CO2 were detected with higher production in TiO2.
The abovementioned metal-oxide is the most common material used as a photocatalyst for photocatalytic methane to methanol conversion. However, it is also worth mentioning metal-organic frameworks (MOFs) as photocatalysts, although the application of MOFs is still limited compared to metal oxide. MOFs consist of metal ions or clusters coordinated to organic ligands or linkers. It has emerged as a photocatalyst owing to its structural characteristic of large surface area, well-ordered porous structure and tunable organic linkers/metal clusters. Those properties endow promising photophysical/chemical properties to facilitate adsorption of CH4 onto the catalyst surface, charge separation and reactant activation [67,68]. A study about photo-oxidation of methane to methanol using MOFs as photocatalysts is reported by An [69] over mono-iron hydroxyl sites immobilized within a metal-organic framework, PMOF-RuFe(OH). A remarkable selectivity was shown that methane was converted to methanol with 100% selectivity and a yield of 8.81 ± 0.34 mmol gcat − h − . The mono-Fe III species acts as a binding and activation site for CH4. However, MOFs have some important issues needed for further improvements, such as poor electronic conductivity, which hampers the charge transfer from organic linker to metal cluster and poor stability during the photocatalytic reaction [70].

Modified Semiconductor
As discussed above, pure semiconductors generally cannot exhibit the excellent properties required to support photocatalytic reactions. In addition, critical properties, such as narrow absorption spectra, low photon quantum efficiency, and easy The abovementioned metal-oxide is the most common material used as a photocatalyst for photocatalytic methane to methanol conversion. However, it is also worth mentioning metal-organic frameworks (MOFs) as photocatalysts, although the application of MOFs is still limited compared to metal oxide. MOFs consist of metal ions or clusters coordinated to organic ligands or linkers. It has emerged as a photocatalyst owing to its structural characteristic of large surface area, well-ordered porous structure and tunable organic linkers/metal clusters. Those properties endow promising photophysical/chemical properties to facilitate adsorption of CH 4 onto the catalyst surface, charge separation and reactant activation [67,68]. A study about photo-oxidation of methane to methanol using MOFs as photocatalysts is reported by An [69] over mono-iron hydroxyl sites immobilized within a metal-organic framework, PMOF-RuFe(OH). A remarkable selectivity was shown that methane was converted to methanol with 100% selectivity and a yield of 8.81 ± 0.34 mmol g cat − h − . The mono-Fe III species acts as a binding and activation site for CH 4 . However, MOFs have some important issues needed for further improvements, such as poor electronic conductivity, which hampers the charge transfer from organic linker to metal cluster and poor stability during the photocatalytic reaction [70].

Modified Semiconductor
As discussed above, pure semiconductors generally cannot exhibit the excellent properties required to support photocatalytic reactions. In addition, critical properties, such as narrow absorption spectra, low photon quantum efficiency, and easy recombination of electrons and holes, become the main drawbacks of neat/pure semiconductors. Thus, several modifications of pure semiconductors have been studied to improve pure semi-conductor properties, including metal/non-metal doping, heterojunction, and crystal facet rearrangement.

Metal/Non-Metal Doping
Elemental doping is a common modification of photocatalysts to optimize its properties by introducing metal or non-metal into the semiconductor. Additional metal plays a role in introducing a new energy level into band structure to extend the light absorption of photocatalysts and help trap electrons or holes, leading to reduced recombination of photogenerated charge carriers [71,72]. Thus, incorporated dopant will enhance the light absorption, regulate band position, and charge carrier process of semiconductors [72]. This section discusses the metal/non-metal doping for each common metal-oxide photocatalyst used in the photo-oxidation of methane to methanol.
Several efforts have been performed to examine the effect of dopants on photocatalyst performance in absorbing light irradiation, visible light in particular. The former study by Taylor [73] used four dopants, including copper, lanthanum, platinum, and a mixture of copper and lanthanum in a WO 3 -based photocatalyst. The structure of the doped WO 3 photocatalyst showed to be more crystalline with a larger crystal and smoother edge. Prior to the study, a reaction without photocatalyst was performed at a temperature between 65 and 95 • C. Conversion of methane and methanol production decreased as temperature decreased, and no photochemical product was observed below 70 • C. Reaction performed with doped semiconductor photocatalyst at temperature 94 • C has successfully converted methane and water to methanol, hydrogen, and acetic acid.
Taylor and Noceti [74] performed the same doped WO 3 photocatalyst, using an additional filter to remove UV components from the lamp. A positive result appeared on the lanthanum doped catalyst that methanol production is higher than non-catalytic reaction. However, platinum and lanthanum/copper exhibited similar results in a noncatalytic reaction. The detrimental effect appeared on copper doped in tungsten oxide inhibited methanol production. In comparing unfiltered and filtered lamp irradiation, experimental platinum doped tungsten oxide showed little difference. This explained that the photocatalyst was operating in visible light the presence of UV light was negligible.
Negishi [25] attempted to activate m-WO 3 and m-TiO 2 by loading the ultrafine metal clusters as cocatalyst on the photocatalysts, including Ag, Ni, and Co. Photocatalyst was synthesized using the hard template method, and metal was loaded using the solid and liquid phase methods. Loading metal clusters have proven to improve the yield of methanol compared to single m-WO 3 ( Figure 16). It happened because loading metal can promote charge separation effectively, and, hence, holes are consumed effectively [75]. The highest methanol yield was shown on the Co n -m-WO 3 because the relationship between the valence band of WO 3 and Co orbital and the relationship between the redox potential of •OH and Co was effective in accelerating the reaction [25]. Atomic-scale gold dispersed in WO3 was fabricated by Yi [76] via a photochemical reduction route. Although gold (Au) is an expensive and scarce noble metal, the utilization of this metal as a cocatalyst is still studied because of its high electronegativity. This catalyst showed a better photocatalytic performance than a gold nanoparticle. Further, it Atomic-scale gold dispersed in WO 3 was fabricated by Yi [76] via a photochemical reduction route. Although gold (Au) is an expensive and scarce noble metal, the utilization of this metal as a cocatalyst is still studied because of its high electronegativity. This catalyst showed a better photocatalytic performance than a gold nanoparticle. Further, it is confirmed that the atomic-scale gold on WO 3 generates the typically active species, such as hydroxyl radical (•OH), hydroperoxyl radical (•OOH), and methyl radical (•CH 3 ), which play an important role in the photocatalytic reaction of methane to methanol.
Despite its outstanding properties, photocatalyst TiO 2 has several drawbacks that limit its application, such as the wide band gap, high recombination rate of electronhole pairs, and the weak separation efficiency of photocarriers [71]. However, modifying its wide band gap and electronic structure of TiO 2 , which bring on poorly visible lightharvesting properties, can reduce massive recombination and improve the interface and surface characteristics [77].
Loading several co-catalysts in the m-TiO 2 by Negishi [25] noticeably showed better photocatalytic activity than pure m-TiO 2 . The highest co-catalytic effect was exhibited by loading cocatalyst Ni in m-TiO 2 with methanol production was around 0.14 µmol·h −1 compared with pure m-TiO 2 , which only generated methanol around 0.02 µmol·h −1 (Figure 17). However, TiO 2 showed a lower methanol generation than WO 3 for both pure and loaded with a co-catalyst. From the experimental results, it can be inferred that the loading of such appropriate co-catalysts effectively improves the activity of photocatalysts [25]. Recently, Wu [78] reported a combination of 2D Titania sheets and atomic-scale Pd species for selective oxidation of methane to methanol. This catalyst is synthesized in 2 steps by solvothermal method to fabricate crystalline 2DT sheets, followed by photochemical reduction to deposit Pd on 2DT. Pd/2DT catalyst exhibited good selectivity and stability in solar light irradiation. Stability is obtained from 2DT that avoids photo-corrosion, and OVs formed in situ in the 2DT material stabilize atomic Pd and suppress the aggregation during methane oxidation. An impressive activity of the catalyst is obtained by the role of Pd in promoting the separation of photo-induced electron-holes and providing active sites for reduction of H 2 O 2 toward the •OH radical.
Some metals have been studied as co-catalysts to modify zinc oxide-based photocatalysts [24,56]. For example, Song et al. [66] studied the selective oxidation of CH 4 to liquid oxygenates using ZnO and some cocatalysts (Pt, Pd, Au, or Ag) at room temperature in water with the addition of O 2 . Up to 125 µ molh −1 of liquid oxygenates, including methanol and formaldehyde, are produced with selectivity higher than 95% over 0.1 wt % Au/ZnO. Efficient and controlled activation of O 2 over cocatalysts has mild reactive oxygen species, •OOH radicals. The •OOH radicals, with the assistance of protonation of water, will enhance the selective liquid oxygenate generation and avoid overoxidation of CH 4 .
The bismuth-based semiconductor is a visible-light responsive photocatalyst that already has narrow band gap energy. Thus, doping may not be considered to be controlled for bismuth-based photocatalysts. To the best of our knowledge, there has been no study report for doping modification in a bismuth-based photocatalyst. However, from several experiments, doping element metal in the photocatalyst can improve the intrinsic properties of the pure semiconductor. Adding an appropriate co-catalyst positively affects photocatalytic activity indicated by enhancing methane conversion, methanol production, or selectivity.
From several studies discussed, adding an appropriate dopant to the photocatalyst has been proven to enhance the photocatalytic activity of the photocatalyst, which is indicated by the improvement of methane conversion, methanol yield, or methanol selectivity compared to pure catalyst. Some metals from base metal (copper, iron, nickel, lead, and zinc) and noble metal (gold, silver, platinum, and palladium) have been extensively studied. Noble metal has been used widely as a catalyst due to its unique intrinsic properties, irreplaceable catalytic activities, good stability, and oxidation resistance. However, the application is still limited to the high cost and the availability. Ultimately, loading dopant will improve the properties of semiconductors, such as enhancing its absorption in visible light, effectively promoting charge separation, and driving to produce preferable species in the reaction.

Heterojunction
Reducing and preventing recombination charge pair carriers have been a concern in the photocatalytic reaction. The recombination process can be illustrated as a person jumping from the surface earth ( Figure 18). The force of gravity will cause the person to fall back to the earth's surface. However, when a bench is available, the person can land and not fall on the ground. This is the same as excited electrons from the valence band. The Coulomb force will cause electrons to return, but electrons will fall in the new conduction band when a conduction band is available from another semiconductor.
Heterojunction modification has been extensively studied as an effort to improve the properties of the semiconductor. It creates an interface between two semiconductors with different band structures to generate a band alignment. There are several types of heterojunctions, including conventional (type I, II, III), type p-n, surface, and direct Z-scheme heterojunction, as shown in Figure 19 [79]. Type II is the most effective heterojunction among conventional heterojunctions because it allows effective electron-hole separation, wide light-absorption range, and fast mass transfer [79]. Type p-n has a more efficient and faster electron-hole separation than type II heterojunction because it creates an internal electric field from the diffusion of the electron from n-type to p-type semiconductor [80]. Different crystal facets on semiconductors have other band structures which can also be used as heterojunctions, similar to that of type II heterojunctions, named surface heterojunctions. One highlight of this heterojunction type is the low cost because it is fabricated from one semiconductor.
Some examples of type II heterojunctions are discussed here. Hameed [32] synthesized WO 3 photocatalyst impregnated with Ag + ion in several proportions (0.1%, 1%, 5%, and 10%) by dissolving AgNO 3 (99.9%) in deionized water and mixed with the appropriate quantity of WO 3 . FE-SEM confirmed the Ag + ion present as Ag 2 O. XPS showed that the surface of Ag 2 O particles resides at surface WO 3 without affecting the morphology base WO 3 ( Figure 20). The more loading Ag + ion into WO 3 , the longer wavelength is shifted on the absorption spectra characterization. It means that loading Ag + can enhance absorption in the visible region. However, in the 10% loading Ag as the highest loading in this experiment, metallic Ag 0 was observed at the inner surface of the photocatalytic reactor, which may be due to the depletion of silver content on the surface, as shown in Figure 20. The photocatalytic charge transfer process using Ag 2 O is shown in Equations (18) and (19).
Combining Ag 2 O (+1.39 V) and WO 3 (+3.1 V) with different band edge positions will generate heterojunction modification that can enhance the lifetime of excited states. The mechanism of an extended lifetime by heterojunction is illustrated in Figure 21. The interface between metal oxide allows the migration of hole (h + ) generated by photon-induced electronic excitation from the valence band of WO 3 to the valence band of Ag 2 O. The electrons (e − ) from the conduction band Ag 2 O will then be transferred to the conduction band of WO 3 . Hydroxyl radical formation can be enhanced by suppressing the charge carrier recombination. The highest methanol production from this process was gained at 5% metal loading in WO 3 . The metal loading higher than 5% affected the proton that it tends to be consumed in dissociation of Ag 2 O than being productive as suppressing recombination species. Heterojunction modification has been extensively studied as an effort to improve the properties of the semiconductor. It creates an interface between two semiconductors with different band structures to generate a band alignment. There are several types of heterojunctions, including conventional (type I, II, III), type p-n, surface, and direct Z-scheme heterojunction, as shown in Figure 19 [79]. Type II is the most effective heterojunction among conventional heterojunctions because it allows effective electron-hole separation, wide light-absorption range, and fast mass transfer [79]. Type p-n has a more efficient and faster electron-hole separation than type II heterojunction because it creates an internal electric field from the diffusion of the electron from n-type to p-type semiconductor [80]. Different crystal facets on semiconductors have other band structures which can also be used as heterojunctions, similar to that of type II heterojunctions, named surface heterojunctions. One highlight of this heterojunction type is the low cost because it is fabricated from one semiconductor. Xie [26] reported metal oxide species anchored on TiO 2 for photocatalytic conversion of methane to methanol at ambient conditions (1 bar and around room temperature) in an aqueous phase system with H 2 O 2 as oxidant. Several metal oxides are Au, PdO x PtO x , Cu 2 O, and FeO x . Iron oxide species showed the best photocatalytic activity, not only high methane conversion (15%) but also high methanol production (>1000 µmol g cat −1 ) obtained (Figure 22), which may be due to a match in Fermi levels, the high dispersity, and small size of the nanoclusters [26]. electric field from the diffusion of the electron from n-type to p-type semiconductor [80]. Different crystal facets on semiconductors have other band structures which can also be used as heterojunctions, similar to that of type II heterojunctions, named surface heterojunctions. One highlight of this heterojunction type is the low cost because it is fabricated from one semiconductor. Some examples of type II heterojunctions are discussed here. Hameed [32] synthesized WO3 photocatalyst impregnated with Ag + ion in several proportions (0.1%, 1%, 5%, and 10%) by dissolving AgNO3 (99.9%) in deionized water and mixed with the appropriate quantity of WO3. FE-SEM confirmed the Ag + ion present as Ag2O. XPS showed that the surface of Ag2O particles resides at surface WO3 without affecting the morphology base WO3 (Figure 20). The more loading Ag + ion into WO3, the longer wavelength is shifted on the absorption spectra characterization. It means that loading Ag + can enhance absorption in the visible region. However, in the 10% loading Ag as the highest loading in this experiment, metallic Ag 0 was observed at the inner surface of the photocatalytic reactor, which may be due to the depletion of silver content on the surface, as shown in Figure 20. The photocatalytic charge transfer process using Ag2O is shown in Equations (18) and (19).
Heterojunction modification can evidently enhance the photocatalytic activity of photocatalysts. Loading another semiconductor will give a new conduction band that can prevent recombination and prolongs the charge carriers' lifetime. However, a suitable combination of photocatalysts and the optimum amount of cocatalysts should be considered to get the maximum result. Combining Ag2O (+1.39 V) and WO3 (+3.1 V) with different band edge positions will generate heterojunction modification that can enhance the lifetime of excited states. The mechanism of an extended lifetime by heterojunction is illustrated in Figure 21. The interface between metal oxide allows the migration of hole (h + ) generated by photon-induced electronic excitation from the valence band of WO3 to the valence band of Ag2O. The electrons (e − ) from the conduction band Ag2O will then be transferred to the conduction band of WO3. Hydroxyl radical formation can be enhanced by suppressing the charge carrier recombination. The highest methanol production from this process was gained at 5% metal loading in WO3. The metal loading higher than 5% affected the proton that it tends to be consumed in dissociation of Ag2O than being productive as suppressing recombination species.   Combining Ag2O (+1.39 V) and WO3 (+3.1 V) with different band edge positions will generate heterojunction modification that can enhance the lifetime of excited states. The mechanism of an extended lifetime by heterojunction is illustrated in Figure 21. The interface between metal oxide allows the migration of hole (h + ) generated by photon-induced electronic excitation from the valence band of WO3 to the valence band of Ag2O. The electrons (e − ) from the conduction band Ag2O will then be transferred to the conduction band of WO3. Hydroxyl radical formation can be enhanced by suppressing the charge carrier recombination. The highest methanol production from this process was gained at 5% metal loading in WO3. The metal loading higher than 5% affected the proton that it tends to be consumed in dissociation of Ag2O than being productive as suppressing recombination species.  Xie [26] reported metal oxide species anchored on TiO2 for photocatalytic conversion of methane to methanol at ambient conditions (1 bar and around room temperature) in an aqueous phase system with H2O2 as oxidant. Several metal oxides are Au, PdOx PtOx, Cu2O, and FeOx. Iron oxide species showed the best photocatalytic activity, not only high methane conversion (15%) but also high methanol production (>1000 μmol gcat −1 ) obtained (Figure 22), which may be due to a match in Fermi levels, the high dispersity, and small size of the nanoclusters [26]. Besides Bi2WO6 and BiVO4, Lopez [65] also evaluated Bi2WO6 coupled with TiO2. Unfortunately, Bi2WO6/TiO2 did not show a better photocatalytic activity than Bi2WO6 and BiVO4, which dominated overoxidation CH4 to CO2. However, Bi2WO6/TiO2 photocatalyst showed higher photocatalytic activity than sole water [65].
Heterojunction modification can evidently enhance the photocatalytic activity of photocatalysts. Loading another semiconductor will give a new conduction band that can prevent recombination and prolongs the charge carriers' lifetime. However, a suitable combination of photocatalysts and the optimum amount of cocatalysts should be considered to get the maximum result.

Structure Modification
Structure modification is another modification that can be applied to improve the properties of the photocatalyst. Structure modification discussed here will be referred to as modification resulting from synthesis, such as crystal structure and formation of mesopore photocatalyst. In addition, the mechanism of the photocatalytic reaction of methane oxidation is also highlighted according to modification on the photocatalyst surface.
Li [82] has successfully synthesized high crystalline WO3 with organized mesopore using PI-b-PEO as a structure-directing agent ( Figure 23). Applying mesopores structure to WO3 photocatalyst has proven to eliminate diffusion limitation so that photocatalytic performance can be enhanced. It might have happened because the high surface area can facilitate access and adsorbed reactants on the surface [82].
High crystalline with ordered mesopores WO3 was studied by Villa [37] for photocatalytic conversion of methane to methanol. The synthesized catalyst characterization found WO3 as a monoclinic structure, consisting of a well-ordered structure with irregularly shaped pores and a surface area of 151 m 2 g −1 .

Structure Modification
Structure modification is another modification that can be applied to improve the properties of the photocatalyst. Structure modification discussed here will be referred to as modification resulting from synthesis, such as crystal structure and formation of mesopore photocatalyst. In addition, the mechanism of the photocatalytic reaction of methane oxidation is also highlighted according to modification on the photocatalyst surface.
Li [82] has successfully synthesized high crystalline WO 3 with organized mesopore using PI-b-PEO as a structure-directing agent ( Figure 23). Applying mesopores structure to WO 3 photocatalyst has proven to eliminate diffusion limitation so that photocatalytic performance can be enhanced. It might have happened because the high surface area can facilitate access and adsorbed reactants on the surface [82]. Adding H2O2 to the reaction system contained the ordered mesopores WO3 exh a higher methanol yield than single mesopore WO3. It proved that with a larger su area of photocatalyst, the more hydroxyl radical could be adsorbed in the catalys consequently will lead to the higher formation of CH3OH [37].
This study substantiated the study of the role of WO3 surface hydroxyl grou the partial photocatalytic oxidation of methane to methanol by Villa [24]. Further this research concluded that OH radical groups on the catalyst surface are mainly re sible for enhancing the performance of WO3 in the selective oxidation of methane to anol [24].

Crystal Facet Re-Arrangements
Photocatalytic activity of semiconductors cannot disregard in the surface a structure tuning. The modifying surface structure of the semiconductor is intended just the exposed facets. Crystal facet engineering could affect the electronic band stru High crystalline with ordered mesopores WO 3 was studied by Villa [37] for photocatalytic conversion of methane to methanol. The synthesized catalyst characterization found WO 3 as a monoclinic structure, consisting of a well-ordered structure with irregularly shaped pores and a surface area of 151 m 2 g −1 .
Adding H 2 O 2 to the reaction system contained the ordered mesopores WO 3 exhibited a higher methanol yield than single mesopore WO 3 . It proved that with a larger surface area of photocatalyst, the more hydroxyl radical could be adsorbed in the catalyst and consequently will lead to the higher formation of CH 3 OH [37].
This study substantiated the study of the role of WO 3 surface hydroxyl groups for the partial photocatalytic oxidation of methane to methanol by Villa [24]. Furthermore, this research concluded that OH radical groups on the catalyst surface are mainly responsible for enhancing the performance of WO 3 in the selective oxidation of methane to methanol [24].

Crystal Facet Re-Arrangements
Photocatalytic activity of semiconductors cannot disregard in the surface atomic structure tuning. The modifying surface structure of the semiconductor is intended to adjust the exposed facets. Crystal facet engineering could affect the electronic band structure, charge transfer, and separation by tuning the surface free energy, formation of hetero/homojunction, and effective mass of hole/electrons [83]. Since the modification is applied on the surface of semiconductors, crystal facet re-arrangements are considered surface heterojunction.
Anatase TiO 2 has some fundamental exposed  Figure 24). This result was believed to be from the role of {001} in avoiding the formation of •CH 3 and •OH, which contribute to methanol overoxidation [85]. Zhu [86] reported that controlling the crystal facet of BiVO4 microcrystal enhanced methane to methanol conversion into a bipyramid, a thick platelet, and a thin platelet shape prepared by hydrothermal synthesis (Figure 25). Referring to the XRD and Raman spectroscopy characterization, the synthesized BiVO4 was found as a monoclinic phase. The surface area measured using the BET method for bipyramid, thick platelet, and thin platelet were determined to be 3.2 m 2 g −1 , 3.6 m 2 g −1, and 3.6 m 2 g −1 , respectively.
The reaction was conducted at a temperature of 65 °C using a Xenon arc lamp (350 W), and the products CH3OH, CO2, and H2 were measured in the reaction. The highest activity was achieved for the BiVO4 bipyramids with 151.7 μmol h −1 g −1 at 2 h reaction time. Similar selectivity emerged on the bipyramid and thick platelet with 85.0% and 85.7%, respectively. Thin platelets showed high activity for water oxidation [87] otherwise, thin platelets produced a large amount of CO2 rather than CH3OH as the main product in this experiment.
From such a result, it was believed that the bipyramid possesses an efficient extraction of holes on the entire surface and intermediate surface reactivity, leading to high methanol selectivity [86]. On the other hand, thinner BiVO4 has a strong oxidation ability [87]. Zhu [86] reported that controlling the crystal facet of BiVO 4 microcrystal enhanced methane to methanol conversion into a bipyramid, a thick platelet, and a thin platelet shape prepared by hydrothermal synthesis (Figure 25). Referring to the XRD and Raman spectroscopy characterization, the synthesized BiVO 4 was found as a monoclinic phase. The surface area measured using the BET method for bipyramid, thick platelet, and thin platelet were determined to be 3.2 m 2 g −1 , 3.6 m 2 g −1, and 3.6 m 2 g −1 , respectively.
The reaction was conducted at a temperature of 65 • C using a Xenon arc lamp (350 W), and the products CH 3 OH, CO 2 , and H 2 were measured in the reaction. The highest activity was achieved for the BiVO 4 bipyramids with 151.7 µmol h −1 g −1 at 2 h reaction time. Similar selectivity emerged on the bipyramid and thick platelet with 85.0% and 85.7%, respectively. Thin platelets showed high activity for water oxidation [87] otherwise, thin platelets produced a large amount of CO 2 rather than CH 3 OH as the main product in this experiment.
respectively. Thin platelets showed high activity for water oxidation [87] otherwise, thin platelets produced a large amount of CO2 rather than CH3OH as the main product in this experiment.
From such a result, it was believed that the bipyramid possesses an efficient extraction of holes on the entire surface and intermediate surface reactivity, leading to high methanol selectivity [86]. On the other hand, thinner BiVO4 has a strong oxidation ability [87].  From such a result, it was believed that the bipyramid possesses an efficient extraction of holes on the entire surface and intermediate surface reactivity, leading to high methanol selectivity [86]. On the other hand, thinner BiVO 4 has a strong oxidation ability [87].
To the best of our knowledge, no study has reported on the crystal facet re-arrangement of WO 3 for photocatalytic conversion of methane to methanol. However, crystal facet engineering has become a potential modification in a photocatalyst. Photocatalysts enclosed with preferred index facets in high percentages could significantly improve their photocatalytic activity. Furthermore, it was proven by some studies conducted for photocatalytic oxidation of methane to methanol that the selectivity of methanol can be enhanced.

Electron Scavenger
Some photocatalytic for methane conversion to methanol reported so far employ an electron scavenger. The addition of electron scavengers has been shown to affect the photocatalytic activity and selectivity of methanol significantly. For example, Villa [37] reported using several electron scavengers, including Fe 3+ , Cu 2+, and Ag + (Figure 26). Significant improvement in methanol yield was shown by a particular additional amount of Fe 3+ and Cu 2+ by a factor of 2.5 and 1.7, respectively. Contrary, the Ag + showed a detrimental effect on methanol generation compared to single WO 3 . Moreover, Ag deposited emerged on the surface of the catalyst during the reaction. To the best of our knowledge, no study has reported on the crystal facet re-arrangement of WO3 for photocatalytic conversion of methane to methanol. However, crystal facet engineering has become a potential modification in a photocatalyst. Photocatalysts enclosed with preferred index facets in high percentages could significantly improve their photocatalytic activity. Furthermore, it was proven by some studies conducted for photocatalytic oxidation of methane to methanol that the selectivity of methanol can be enhanced.

Electron Scavenger
Some photocatalytic for methane conversion to methanol reported so far employ an electron scavenger. The addition of electron scavengers has been shown to affect the photocatalytic activity and selectivity of methanol significantly. For example, Villa [37] reported using several electron scavengers, including Fe 3+ , Cu 2+, and Ag + (Figure 26). Significant improvement in methanol yield was shown by a particular additional amount of Fe 3+ and Cu 2+ by a factor of 2.5 and 1.7, respectively. Contrary, the Ag + showed a detrimental effect on methanol generation compared to single WO3. Moreover, Ag deposited emerged on the surface of the catalyst during the reaction. Zeng [27] studied the synergetic effect of Fe 2+ and H2O2 called the Fenton reaction to the photocatalytic reaction for several photocatalysts, including Fe2O3 and TiO2 NiO, CuO, ZnO, and WO3. Photocatalyst TiO2 showed the highest yield for methanol, while photocatalyst WO3 showed the highest yield for formic acid (Figure 27). This experimental re- Zeng [27] studied the synergetic effect of Fe 2+ and H 2 O 2 called the Fenton reaction to the photocatalytic reaction for several photocatalysts, including Fe 2 O 3 and TiO 2 NiO, CuO, ZnO, and WO 3 . Photocatalyst TiO 2 showed the highest yield for methanol, while photocatalyst WO 3 showed the highest yield for formic acid (Figure 27). This experimental result exhibited that adding appropriate Fenton reagents will contribute to methane conversion and methanol selectivity [27].
Electron scavenger can leverage the photocatalytic reaction because this species will capture the electron so that recombination of charge carrier (e − and h + ) can be avoided and methanol yield will enhance simultaneously [88]. Furthermore, adding Fe 3+ ions in the reaction can inhibit the generation of •O 2 − by capturing electrons in the conduction band to form Fe 2+ [29]. The electron scavenger is also an appealing modification for the photocatalytic reaction because this method is relatively simple and cost-effective [23,33].
Zeng [27] has successfully achieved a highly selective conversion of methane to methanol through photocatalysis-Fenton (Fe 2+ and H 2 O 2 ) reaction with solar energy at room temperature. The Fenton reaction was carried out under solar light irradiation. Methane with a pressure of 3 MPa was injected into the reactor, and the suspension temperature was maintained at 30 • C. As a result, excellent photocatalytic activity was achieved using TiO 2 photocatalyst with methanol yield and selectivity of 471 µmol g −1 h −1 ( Figure 27) and 83% (Figure 28), respectively. icant improvement in methanol yield was shown by a particular additional amount of Fe 3+ and Cu 2+ by a factor of 2.5 and 1.7, respectively. Contrary, the Ag + showed a detrimental effect on methanol generation compared to single WO3. Moreover, Ag deposited emerged on the surface of the catalyst during the reaction. Zeng [27] studied the synergetic effect of Fe 2+ and H2O2 called the Fenton reaction to the photocatalytic reaction for several photocatalysts, including Fe2O3 and TiO2 NiO, CuO, ZnO, and WO3. Photocatalyst TiO2 showed the highest yield for methanol, while photocatalyst WO3 showed the highest yield for formic acid ( Figure 27). This experimental result exhibited that adding appropriate Fenton reagents will contribute to methane conversion and methanol selectivity [27].  Electron scavenger can leverage the photocatalytic reaction because this species will capture the electron so that recombination of charge carrier (e − and h + ) can be avoided and methanol yield will enhance simultaneously [88]. Furthermore, adding Fe 3+ ions in the reaction can inhibit the generation of •O2 − by capturing electrons in the conduction band to form Fe 2+ [29]. The electron scavenger is also an appealing modification for the photocatalytic reaction because this method is relatively simple and cost-effective [23,33].
Zeng [27] has successfully achieved a highly selective conversion of methane to methanol through photocatalysis-Fenton (Fe 2+ and H2O2) reaction with solar energy at room temperature. The Fenton reaction was carried out under solar light irradiation. Methane with a pressure of 3 MPa was injected into the reactor, and the suspension temperature was maintained at 30 °C. As a result, excellent photocatalytic activity was achieved using TiO2 photocatalyst with methanol yield and selectivity of 471 μmol g −1 h −1 ( Figure 27) and 83% ( Figure 28), respectively. It was believed to have occurred due to the band structure of TiO2, which exactly matches well with the redox potentials of H2O2/•OH, H2O/•OH, and O2/•O2 − and the Fenton reaction promoted the closed cycle (Fe 3+ + e ⟶ Fe 2+ ) and iron restoration ( Figure 29).  It was believed to have occurred due to the band structure of TiO2, which exactly matches well with the redox potentials of H2O2/•OH, H2O/•OH, and O2/•O2 − and the Fenton reaction promoted the closed cycle (Fe 3+ + e ⟶ Fe 2+ ) and iron restoration ( Figure 29). In evaluating bismuth-based synthesis for selective photoactivation of methane conducted by Lopez [65], two-electron scavengers O2 and Fe 3+ were introduced to the photocatalyst Bi2WO6 system. Adding electron scavengers for both O2 and Fe 3+ showed a similar behavior that no change of color observed at the end of the test, indicating that O2 can serve as electron trapping and Fe 3+ can inhibit self-reduction of Bi2WO6 [65]. However, adding Fe 3+ aggravated the selectivity of methanol since CO2 dominated CH4 In evaluating bismuth-based synthesis for selective photoactivation of methane conducted by Lopez [65], two-electron scavengers O 2 and Fe 3+ were introduced to the photocatalyst Bi 2 WO 6 system. Adding electron scavengers for both O 2 and Fe 3+ showed a similar behavior that no change of color observed at the end of the test, indicating that O 2 can serve as electron trapping and Fe 3+ can inhibit self-reduction of Bi 2 WO 6 [65]. However, adding Fe 3+ aggravated the selectivity of methanol since CO 2 dominated CH4 overoxidation, which can be due to Fe 3+ improved electron transfer, enhanced charge separation, and produced higher hydroxyl radical [65].
Besides the electron, it is also essential to trap •OH in the photocatalytic system, as Lopez [88] reported using nitrite ion. Hydroxyl radical is crucial to produce methyl radical, but excessive •OH could lead to aggravation of methanol selectivity. Thus, additional nitrite ions in the photocatalytic system containing BiVO 4 could improve the selectivity of methanol than pure only BiVO 4 .
The addition of electron scavengers offered a more accessible and cost-effective way to achieve the same benefit as the co-catalyst [27]. Iron oxide species are the most active electron scavenger for photocatalytic methane oxidation to methanol compared with other metals [27,29,37]. Iron species have some roles in this process, such as an electron acceptor to prevent recombination of charge pairs and inhibit the generation of •O 2 − to overoxidized methanol. Table 3 shows recent progress on development of neat and modified photocatalysts for photocatalytic oxidation of methane to methanol with various synthesis method; operating condition including photocatalyst loading, reactant, light source, operating pressure and temperature, reactor type; in conjunction with photocatalytic performance including yield, conversion, and selectivity.    It is essential to choose an appropriate co-catalyst for photocatalyst to improve the photocatalytic activity Particle size 1 nm in this study was considered not optimal for promoting the reaction   The semiconductor has a unique electronic property that will allow the electron to exit upon given appropriate energy. Therefore, for photocatalytic application, energy as a driving force is provided in the form of light irradiation. This phenomenon can occur due to the presence of a band gap in the semiconductor. The band gap is a gap between the valence and conduction bands where no electrons can reside or is also called a forbidden gap.
As explained before, upon illumination of appropriate light with the same or higher energy than the band gap, electrons will excite from the valence band to the conduction band. Consequently, generating electrons (e − ) in the conduction. The band gap value can be calculated by applying the Kubelka-Munk function, as shown in Equation (20) [90].
E g = Band gap energy (eV) h = Planck's constant α = Extinction coefficient v = Light frequency (s −1 ) n = 2 (for indirect allowed transition) n = 3 (for indirect forbidden transition) n = 1 2 (for direct allowed transition) n = 3/2 (for direct forbidden transition) Another method for band gap determination was proposed by Zanatta [91] by fitting a sigmoid (Boltzmann) function to the semiconductor's corresponding optical. This method is claimed to be more accurate and straightforward than the traditional approaches.
A semiconductor with a wide band gap absorbs the UV light spectrum, while a low band gap absorbs visible light. However, some semiconductors can only effectively absorb light under UV light. Therefore, an effort has been focused on decreasing the band gap of the photocatalyst. Thus, visible light can be used instead of UV light by doping the semiconductor with another metal or non-metal.
The critical consideration in selecting the photocatalyst for the photocatalytic reaction is the position of the photocatalyst band gap that can produce the intended species for reaction. Methanol production from methane photooxidation can be produced either by species O 2 or •OH produced from H 2 O and H 2 O 2 . Thus, among several photocatalysts, TiO 2 and WO 3 have been commonly used in this process because they have the most suitable band gap position to produce the required species for reaction ( Figure 30). However, O 2 is a strong oxidant that could lead to over oxidation of methanol produced in the system. The band gap position of WO 3 is unsuitable for degrading methanol via oxidation by O 2 . It could be why the WO 3 is the most frequent photocatalyst studied in methanol production from methane photooxidation.

Morphology and Specific Surface Area
The morphology of photocatalysts is one factor that strongly affects photocatalytic performance [92]. Reactants should overcome the diffusion limitation upon reaching the surface of the photocatalyst, and sometimes it becomes the limiting step during the photocatalytic process. Controlled pore size and high surface area photocatalyst can facilitate the reactant to access the surface easily. Hence, photocatalytic performance can be maximized [93]. Porous materials are classified into several kinds by their size, including microporous (<2 nm), mesoporous (2-50 nm), and macroporous (>50 nm) [94]. The mesoand macropore sizes are desirable because these pore sizes are considered to facilitate the diffusion of the molecule [95].
Mesopore photocatalyst in ordered channels is highly photocatalytic because it can facilitate fast intraparticle molecular transfer to decrease charge recombination [37]. In addition, pore connectivity in the porous material leads to the large surface of synthesized ordered m-WO3. The hierarchically porous materials and ordered nanostructure have overcome mass transport limitations [82,96]. In terms of pore arrangement, ordered mesopores show higher activity than disorder mesoporous [92] because the ordered mesoporous can enhance light harvesting from a deeper light penetration and light scattering in the pore channels facilitate diffusion and adsorption of the reactant [97].
The crystallinity of photocatalysts is also essential to improving the properties and activity of photocatalysts. Improving the crystallinity of photocatalysts can prevent charge recombination from occurring [98]. Several studies have proven that high crystallinity can improve photocatalytic activity, leading to a higher yield of product [82,99,100], Thus, the synergistic effect of high crystallinity and ordered mesoporous channels could significantly reduce the electron-hole pair recombination to obtain a higher photocatalytic activity

Crystal Facets
Surface engineering with an optimized reactive facet is a practical approach to optimizing photocatalytic activity for energy conversion and environmental remediation [83,87,101,102]. Over the past decade, significant efforts have been made to explore and understand the effect of optimizing semiconductor reactive facet in the photocatalytic activity for various applications such as water splitting [103][104][105], CO2 reduction [106,107],

Morphology and Specific Surface Area
The morphology of photocatalysts is one factor that strongly affects photocatalytic performance [92]. Reactants should overcome the diffusion limitation upon reaching the surface of the photocatalyst, and sometimes it becomes the limiting step during the photocatalytic process. Controlled pore size and high surface area photocatalyst can facilitate the reactant to access the surface easily. Hence, photocatalytic performance can be maximized [93]. Porous materials are classified into several kinds by their size, including microporous (<2 nm), mesoporous (2-50 nm), and macroporous (>50 nm) [94]. The mesoand macropore sizes are desirable because these pore sizes are considered to facilitate the diffusion of the molecule [95].
Mesopore photocatalyst in ordered channels is highly photocatalytic because it can facilitate fast intraparticle molecular transfer to decrease charge recombination [37]. In addition, pore connectivity in the porous material leads to the large surface of synthesized ordered m-WO 3 . The hierarchically porous materials and ordered nanostructure have overcome mass transport limitations [82,96]. In terms of pore arrangement, ordered mesopores show higher activity than disorder mesoporous [92] because the ordered mesoporous can enhance light harvesting from a deeper light penetration and light scattering in the pore channels facilitate diffusion and adsorption of the reactant [97].
The crystallinity of photocatalysts is also essential to improving the properties and activity of photocatalysts. Improving the crystallinity of photocatalysts can prevent charge recombination from occurring [98]. Several studies have proven that high crystallinity can improve photocatalytic activity, leading to a higher yield of product [82,99,100], Thus, the synergistic effect of high crystallinity and ordered mesoporous channels could significantly reduce the electron-hole pair recombination to obtain a higher photocatalytic activity.

Crystal Facets
Surface engineering with an optimized reactive facet is a practical approach to optimizing photocatalytic activity for energy conversion and environmental remediation [83,87,101,102]. Over the past decade, significant efforts have been made to explore and understand the effect of optimizing semiconductor reactive facet in the photocatalytic activity for various applications such as water splitting [103][104][105], CO 2 reduction [106,107], photodegradation organic pollutant [108], and antibacterial activity [109]. For instance, optimizing high exposure of reactive [001] facet from anatase TiO 2 was shown to be effective in improving the production of H 2 [87] and degrading organic contaminants [104]. Furthermore, Xie [110] demonstrated that a [002] dominant rectangular sheet-like WO 3 crystal could elevate photocatalytic reduction of CO 2 to CH 4 .
Many photocatalytic functions are improved through crystal facet engineering, such as surface energy, electronic band structure, charge transfer and separation, reactant adsorption and product desorption, and surface redox [83]. For example, the domination of exposed [001] TiO 2 facets reduced electron holes recombination rate by capturing photoelectron and elevated surface energy, favoring photocatalytic oxidation [97]. Furthermore, Yu [111] reported that TiO 2 contained with exposed 58% [001] and 42% [101] had the highest activity for CO 2 photoreduction because the combination of exposed [101] and [101] facets can form surface heterojunction within a single TiO 2 . Besides favoring the separation of photo-generated carriers and enhanced photocatalytic activity [106], surface heterojunction is economically preferable since only one semiconductor is used [79].
Tailoring faceted TiO 2 can be established by many synthesis methods, including the wet-chemistry route (hydrothermal, solvothermal, and nonhydrolytic), gas oxidation route, topotactic transformation, crystallization transformation from amorphous TiO 2 , epitaxial growth, and spray-drying [112]. However, the most used methods are hydrothermal and solvothermal due to flexibility in manipulating crystal nucleation and growth behavior [103]. Anatase TiO 2 crystals are naturally dominated by a less reactive and stable surface [109,113]. Therefore, the key to this method is controlling crystal shape evolution during growth until desired facets can be reached using an appropriate capping agent [114].
Although many intensive experimental and theoretical methods have been studied for surface engineering of crystal facet exposure, their application has not been intensely studied in the photocatalytic conversion of methane to methanol. To our knowledge, only BiVO 4 [86] and, recently, TiO 2 [85] were explored for methane's photooxidation. The remarkable results were shown by those studied. Thus, further studies investigating the crystal facet engineering of other photocatalysts concomitantly to explore the synergistic effect of other modifications such as adding H 2 O 2 , electron scavenger, and element doping will be beneficial for the photocatalytic generation of methanol.

Defect Sites
Solar radiation has a light wavelength from 280 to 4000 nm and consists mainly of 6.6% of ultraviolet radiation (<380 nm), 44.7% of visible radiation (380-780 nm), and 48.7% of infrared radiation (>780 nm) [115]. Therefore, the photocatalyst is desired to absorb abundantly available solar energy. However, sunlight comprises light in visible and near-infrared regions with lower energy than UV light and can reduce photocatalyst performance. Thus, modification is needed to improve photocatalyst absorptivity.
Doping is a familiar modification in photocatalysts to activate poor visible light under visible-light irradiation using metal or non-metal elements. By definition, doping modification incorporates atoms or ions in a crystalline lattice, i.e., modification of the bulk structure of crystallites, but not a change of surfaces [115]. Furthermore, the doped ion can facilitate carriers to diffuse to the surface by introducing additional energy levels into the band structure that will be used to trap electrons and holes [71]. Therefore, by adding a dopant, such as iron species, in the TiO 2 , some photocatalyst properties are enhanced, including the electron-hole separation, lowering the reduction potential of H 2 O 2 and also avoiding oxygen reduction to •O 2 − [116].

Catalyst Loading
Loading catalyst is one of the factors that can affect the rate of photocatalytic reaction. The concentration used varies between 0.5 g/L to 10 g/L. Gondal [29] studied the effect of various catalyst loading in the photooxidation of methane to methanol in three different laser powers. It showed the dependence of methanol yield on the varied catalyst concentration ( Figure 31).

Catalyst Loading
Loading catalyst is one of the factors that can affect the rate of photocatalytic reaction. The concentration used varies between 0.5 g/L to 10 g/L. Gondal [29] studied the effect of various catalyst loading in the photooxidation of methane to methanol in three different laser powers. It showed the dependence of methanol yield on the varied catalyst concentration ( Figure 31). Methanol yield increased as catalyst concentration increased. In a particular concentration, it reached a maximum yield of methanol and then gradually decreased. Therefore, there is an optimum methanol yield for photocatalyst loading. Thus, an appropriate amount of photocatalyst will be effective in enhancing photocatalytic activity.
However, loading excessive catalysts will diminish the photocatalytic activity of a reaction. Such a result is believed that increasing the catalyst particle density beyond the optimum value will facilitate the recombination of electron-hole pairs [29]. Furthermore, in excessive catalyst loading, light cannot enter to activate the catalyst particle, which may scatter the photons and obstruct the light absorption [26]. Therefore, catalyst concentration substantially will increase the reaction rate, but the reaction rate will decrease [52].

Light Wavelength and Intensity
Light is a driving force in the photocatalytic reaction to activate the photocatalyst and initiate the photocatalytic reaction. Commonly, light sources can be obtained by the conventional lamp (Xenon lamp or mercury lamp) or intense high lamp (laser lamp). However, using light from sunlight, mostly visible light, is the ultimate purpose of photocatalytic reaction. Therefore, a filter separates the UV and the Visible light from the light source in the experimental study.
Gondal [29] performed different flux densities ranging from 0.5-3 Watt, resulting in a dependency of flux density on methanol production (Figure 32a). A gradual increase in methanol yield with the flux density because a more significant amount of photons is generated to produce hydroxyl radicals. However, it decreased at a constant value after reaching the maximum point, indicating equal generation of hydroxyl radicals and recombination of electron-hole pairs. Thus, high flux density may not effectively exploit the photon generated from light since most photons escape from the reaction vessel without Methanol yield increased as catalyst concentration increased. In a particular concentration, it reached a maximum yield of methanol and then gradually decreased. Therefore, there is an optimum methanol yield for photocatalyst loading. Thus, an appropriate amount of photocatalyst will be effective in enhancing photocatalytic activity.
However, loading excessive catalysts will diminish the photocatalytic activity of a reaction. Such a result is believed that increasing the catalyst particle density beyond the optimum value will facilitate the recombination of electron-hole pairs [29]. Furthermore, in excessive catalyst loading, light cannot enter to activate the catalyst particle, which may scatter the photons and obstruct the light absorption [26]. Therefore, catalyst concentration substantially will increase the reaction rate, but the reaction rate will decrease [52].

Light Wavelength and Intensity
Light is a driving force in the photocatalytic reaction to activate the photocatalyst and initiate the photocatalytic reaction. Commonly, light sources can be obtained by the conventional lamp (Xenon lamp or mercury lamp) or intense high lamp (laser lamp). However, using light from sunlight, mostly visible light, is the ultimate purpose of photocatalytic reaction. Therefore, a filter separates the UV and the Visible light from the light source in the experimental study.
Gondal [29] performed different flux densities ranging from 0.5-3 Watt, resulting in a dependency of flux density on methanol production (Figure 32a). A gradual increase in methanol yield with the flux density because a more significant amount of photons is generated to produce hydroxyl radicals. However, it decreased at a constant value after reaching the maximum point, indicating equal generation of hydroxyl radicals and recombination of electron-hole pairs. Thus, high flux density may not effectively exploit the photon generated from light since most photons escape from the reaction vessel without interaction with the catalyst. In contrast, recombination of electron-hole pairs and scattering are prominent processes for low flux density.
interaction with the catalyst. In contrast, recombination of electron-hole pairs and scattering are prominent processes for low flux density. Shi et al. [117] performed photocatalytic methane to methanol on a fluffy metal-free carbon nitride photocatalyst in the presence of H2O2 using simulated AM1.5G and visible light >420 nm. Visible light showed a lower methane conversion than that under full sunlight (Figure 32b). Under full simulated sunlight irradiation, •OH was generated from strong photolysis of H2O2, whereas under visible light irradiation •OH was produced by photocatalytic reduction of H2O2 by photoexcited electrons (e − ).

Irradiation Time
The irradiation time is one of the crucial factors in the photocatalytic methane conversion to methanol. Generally, the amount of product will increase as reaction time increase since more reactant can be contacted with the catalyst. However, it does not fully apply to methanol generation from methane and water. This is because methanol, as the product, is more reactive than methane as the reactant. Thus, sufficient time will be needed to achieve the highest methanol production.
Many studies of photocatalytic methanol production from methane, including reaction or irradiation time as a parameter to observe. Commonly, irradiation time varied between 1.5 to 8 h. Besides CH3OH, other side products, such as O2, H2, CO, CO2, and C2H6, were also observed.
In photocatalytic methanol production from methane, the yield of methanol increased until reaching the maximum yield. Then as time increased, the yield or selectivity of methanol gradually decreased ( Figure 33). It can be explained that methanol will compete with water molecules immediately after its formation for photogenerated holes, hence the degradation coincides with the generation of hydroxyl radical [32]. Another reason is reported by Gondal [29], who observed the yield of O2 and CH3OH through reaction. The decrease in methanol production could correspond to the formation of superoxide radicals (O2 − ) from O2 reduction. This superoxide radical further reacts with CH3OH and produces CO2. It is remarked by the depletion of O2 and the lack of methanol (Figure 33a). Shi et al. [117] performed photocatalytic methane to methanol on a fluffy metal-free carbon nitride photocatalyst in the presence of H 2 O 2 using simulated AM1.5G and visible light >420 nm. Visible light showed a lower methane conversion than that under full sunlight (Figure 32b). Under full simulated sunlight irradiation, •OH was generated from strong photolysis of H 2 O 2 , whereas under visible light irradiation •OH was produced by photocatalytic reduction of H 2 O 2 by photoexcited electrons (e − ).

Irradiation Time
The irradiation time is one of the crucial factors in the photocatalytic methane conversion to methanol. Generally, the amount of product will increase as reaction time increase since more reactant can be contacted with the catalyst. However, it does not fully apply to methanol generation from methane and water. This is because methanol, as the product, is more reactive than methane as the reactant. Thus, sufficient time will be needed to achieve the highest methanol production.
Many studies of photocatalytic methanol production from methane, including reaction or irradiation time as a parameter to observe. Commonly, irradiation time varied between 1.5 to 8 h. Besides CH 3 OH, other side products, such as O 2 , H 2 , CO, CO 2 , and C 2 H 6 , were also observed.
In photocatalytic methanol production from methane, the yield of methanol increased until reaching the maximum yield. Then as time increased, the yield or selectivity of methanol gradually decreased ( Figure 33). It can be explained that methanol will compete with water molecules immediately after its formation for photogenerated holes, hence the degradation coincides with the generation of hydroxyl radical [32]. Another reason is reported by Gondal [29], who observed the yield of O 2 and CH 3 OH through reaction. The decrease in methanol production could correspond to the formation of superoxide radicals (O 2 − ) from O 2 reduction. This superoxide radical further reacts with CH 3 OH and produces CO 2 . It is remarked by the depletion of O 2 and the lack of methanol (Figure 33a

Reactor Configuration
The experiment will consist of catalyst synthesis, characterization, and photocatalytic activity study in a typical photocatalytic reaction study. A photocatalytic activity study is performed in the photoreactor, where reaction products are generated from the contact between photocatalysts, reactants, and photons. The reactor used for the photocatalytic process can be a slurry reactor, fixed bed, or membrane photoreactor [118]. The batch slurry reactor is the most frequently used reactor in the photocatalytic production of methanol from methane and water since it can get three phases (gas, liquid, and solid) contacted. In addition, the slurry reactor will provide a high surface area to illuminate and high mass transfer between catalyst and reactant through agitation.
In designing photoreactors, there are some important factors to consider. It will influence photoreactor performance, including the light source, geometrical configuration to accommodate light, the material of construction, heat exchange, and mixing and flow characteristics [119]. The light source type determines the wavelength and intensity range used in the photocatalytic process. A good photoreactor is desired to have a high ability to collect photons that extend the area to be illuminated to achieve an increased activity in the photoreactor [120]. The material used for the photoreactor should handle temperature, pressure, and corrosion problems based on the reactant and operation condition applied. The material for the photoreactor can be quartz, ace glass, or Pyrex. The quartz photoreactor is the most frequently used in the photocatalytic reaction due to its excellent transparency range, particularly in UV light [118]. As energy is added in the form of light, heat increase is inevitable, so it is crucial to remove heat using a heat exchanger to

Reactor Configuration
The experiment will consist of catalyst synthesis, characterization, and photocatalytic activity study in a typical photocatalytic reaction study. A photocatalytic activity study is performed in the photoreactor, where reaction products are generated from the contact between photocatalysts, reactants, and photons. The reactor used for the photocatalytic process can be a slurry reactor, fixed bed, or membrane photoreactor [118]. The batch slurry reactor is the most frequently used reactor in the photocatalytic production of methanol from methane and water since it can get three phases (gas, liquid, and solid) contacted. In addition, the slurry reactor will provide a high surface area to illuminate and high mass transfer between catalyst and reactant through agitation.
In designing photoreactors, there are some important factors to consider. It will influence photoreactor performance, including the light source, geometrical configuration to accommodate light, the material of construction, heat exchange, and mixing and flow characteristics [119]. The light source type determines the wavelength and intensity range used in the photocatalytic process. A good photoreactor is desired to have a high ability to collect photons that extend the area to be illuminated to achieve an increased activity in the photoreactor [120]. The material used for the photoreactor should handle temperature, pressure, and corrosion problems based on the reactant and operation condition applied. The material for the photoreactor can be quartz, ace glass, or Pyrex. The quartz photoreactor is the most frequently used in the photocatalytic reaction due to its excellent transparency range, particularly in UV light [118]. As energy is added in the form of light, heat increase is inevitable, so it is crucial to remove heat using a heat exchanger to maintain the desired temperature. Mixing characteristics is also vital in designing photoreactors to provide high contact between reactants and catalysts. The easiest method for a liquid-solid photoreactor to agitate the mixture is by using a stirrer [119].
In the photocatalytic reaction, the particle should highly absorb the light participation in the reaction to achieve a high degree of substance conversion [121]. Therefore, lamp position is one of the factors which will influence the capability of light-harvesting in the photocatalyst. In typical slurry reactors, photoreactors can be classified into several types based on their lamp position; (a) Immerse illuminated (Figure 34a), (b) Side illuminated (Figure 34b), and (c) Top illuminated (Figure 34c). Table 4 summarizes the advantages and disadvantages of each lamp position for photocatalytic reaction.
Molecules 2022, 27, x FOR PEER REVIEW 40 of 47 maintain the desired temperature. Mixing characteristics is also vital in designing photoreactors to provide high contact between reactants and catalysts. The easiest method for a liquid-solid photoreactor to agitate the mixture is by using a stirrer [119].
In the photocatalytic reaction, the particle should highly absorb the light participation in the reaction to achieve a high degree of substance conversion [121]. Therefore, lamp position is one of the factors which will influence the capability of light-harvesting in the photocatalyst. In typical slurry reactors, photoreactors can be classified into several types based on their lamp position; (a) Immerse illuminated (Figure 34a), (b) Side illuminated (Figure 34b), and (c) Top illuminated (Figure 34c). Table 4 summarizes the advantages and disadvantages of each lamp position for photocatalytic reaction.   Table 4. Advantages and disadvantages of various types of photoreactor illumination [118]. Reproduced with permission from Khan and Tahir. Copyright © 2022 Elsevier.

Light Position Advantages Disadvantages
Top illuminated -Exploits higher light irradiation compared to side illumination -Good exploitation of light as when irradiations fall to the bottom of the reactor can reflect back -The color of the solution will affect the irradiation as dark color is difficult to pass through the slurry Side illuminated -Easy to install -Suitable for photoreactors that do not need a deep penetration -Uneven illumination as only one side will have higher irradiation -Good illumination will be achieved if the reactor irradiates from all sides, but this will consume high energy - The glass can scatter the light Immerse illuminated - Most frequently used - The higher area of illumination compares to side and top illumination -Complex installation - The lamp in the middle of the slurry will affect the unequal mixing - The particle may stick to the inner tube - The use of sunlight will not be a possible inefficient way

Conclusions and Future Perspective
Converting methane into higher chemical values such as methanol is an exciting prospect in the industry. Currently, methanol is produced industrially by steam reforming, which consumes high energy for syngas intermediate product and is economically not preferable. Photocatalytic technology has shown remarkable potential as a low-cost, environmentally-friendly, and sustainable technology. A thermodynamically unfavorable reaction can be performed in mild conditions using a photocatalytic reaction. The utilization of methane, water, and light which are abundant and inexpensive, to produce methanol will be a remarkable breakthrough as new energy. Many efforts have been made in this area and produced many insightful research types. However, it still encounters challenges that limit the photocatalytic reaction effectivity and application.
Current studies on the photocatalytic conversion of methane to methanol commonly strive for a high-efficiency photocatalytic reaction (high methane conversion, methanol yield, and methanol selectivity). Selective oxidation of methane to methanol has often been considered a "holy grail" reaction in catalysis. Such a low-efficiency reaction is believed to be happened due to the stable and low polarization of methane. It leads methane to be difficult to activate and thus limits the conversion of methane. Water is used as an oxidant in a typical photocatalytic reaction of methane to methanol. Upon reaction, methane gas and an inert gas (Helium, Argon, and Nitrogen) will be purged into the photoreactor or sparged into the water for a specific duration to get a saturated mixture of water and methane. In this case, methane also has low solubility in the water (~24.4 mg/L), limiting the conversion [122]. In some studies, high pressure of methane was applied, and noticeably higher methanol yield could be achieved [27]. Since the low solubility of methane in water negatively affects the selective oxidation of methane to methanol, the study in the gas-phase condition may be considered by using humified methane [123] or oxygen as the oxidant. However, it is essential to consider that oxygen is also a more potent oxidant than water, leading to methanol overoxidation [65].
Methanol overoxidation in this reaction also becomes one of the challenges. Methanol as the product is naturally more reactive than methane as a reactant. Therefore, Overoxidation of methanol may happen when a certain amount of methanol competes with water for holes in the valence band or overoxidation by oxygen or radical superoxide [32,124]. Thus, a moderate oxidation power photocatalyst is believed to be able to prevent overoxidation of methanol such as WO 3 [37], bipyramid BiVO 4 [86], and {001}-dominated TiO 2 [85]. Furthermore, adding iron species can enhance the selectivity of methanol by lowering the reduction potential of H 2 O 2 and avoiding oxygen reduction to radical superoxide for TiO 2 [26].
Furthermore, short reaction times by adding sufficient H 2 O 2 should be considered to get the optimal yield of methanol [31]. To prevent methanol overoxidation, the system should be kept so that the methanol amount will not be sufficient to compete with water for holes in the valence band. Therefore, the development of gas-solid reaction [123] and the continued process should be considered a priority in future development.
The vast majority of photocatalytic studies are one-dimensional studies that only consider the effect of one parameter. However, it can lead to bias or misinterpretation since the study cannot thoroughly investigate the impact of more than one parameter [125]. Thus, a study of the synergistic effect of some parameters is vital to prevent invisible effects for other parameters.
Besides having precise knowledge of all relevant parameter influences in photocatalytic reaction, the kinetic model is also essential to implement this process industrially. Kinetic modeling of heterogeneous photocatalysts can be identified using Langmuir-Hinshelwood type kinetics [126]. The reaction rate by kinetic of Langmuir-Hinshelwood depends on the light intensity, which can be linear or square [29,114]. The rate is linear for low light intensity, while the rate is modeled proportionally to the square root for high intensity. The study of the kinetic model for photocatalytic conversion of methane to methanol is still very limited. Thus, the kinetic model has to be considered in the future development.
The state of the art of the current study in the photocatalytic oxidation of methane to methanol is shown in Table 3. In summary, converting methane to methanol at mild conditions photo catalytically is a promising process with high economic and environmental potential. Although many types of research have been studied in this field, this system still has many challenges. Therefore, some recommendations also have been proposed for future development. The authors hope this paper review will give a clear overview of the recent advance in the photocatalytic conversion of methane to methanol. Therefore, it can help and encourage other researchers to study this promising field. A deep and clear knowledge will trigger fast development, and, ultimately, the process can be applied in large-scale and commercial industries.