Photocatalytic Conversion of Organic Pollutants in Air: Quantum Yields Using a Silver/Nitrogen/TiO 2 Mesoporous Semiconductor under Visible Light

: This research studies the photocatalytic conversion of methanol (25–90 µ mol/L range) as a volatile organic compound (VOC) surrogate into CO 2 , using a N/Ag/TiO 2 photocatalyst under visible light irradiation in a Photo-CREC Air unit. The N/Ag/TiO 2 mesh supported photocatalyst is prepared via the solvothermal method. While the bare-TiO 2 is inactive under visible light, the N/Ag/TiO 2 2 wt.% loaded stainless-steel woven mesh displays 35% quantum yields, with 80% absorbed photons and 60% methanol conversion in a 110 min irradiation period. Results obtained are assigned to silver surface plasmon resonance, silver and nitrogen species synergistic impacts on band gap, and their inﬂuence on particle agglomerate size and semiconductor acidity. The determined quantum yields under visible light in a Photo-CREC Air unit, are the highest reported in the technical literature, that these authors are aware of, with this opening unique opportunity for the use of visible light for the puriﬁcation of air from VOC contaminants. bare ‐ TiO 2 and N/Ag/TiO 2 under Near ‐ UV and Irradiation The photocatalytic oxidation of gas phase methanol in a recirculating batch Pho ‐ to ‐ CREC ‐ Air Reactor was carried out under two different light source illuminations: near ‐ UV and visible light, by using either bare ‐ TiO 2 or N/Ag/TiO 2 coated on a stain ‐ less ‐ steel woven mesh. Various chemical species formed were determined by using a gas chromatograph unit with a flame ionization detector (GC ‐ FID). Supplementary Materials A and B reports a typical GC ‐ FID chromatogram and calibration curves for various photocatalytic methanol conversion products. This chromatogram showed conclusively that there are no other chemical species detected under dark conditions, except the in ‐ jected methanol and the CO 2 contained in the atmosphere at a constant concentration. Figure 5a,b report the photocatalytic conversion of methanol and the formation of formaldehyde and formic acid intermediates, when using the bare ‐ TiO 2 under near ‐ UV and visible light, respectively. The coated bare ‐ TiO 2 in Figure 5a shows an excellent photocatalytic activity under the near ‐ UV light irradiation, with rapid methanol degra ‐ dation and essentially zero methanol concentration achieved in 110 min of irradiation time. One can also notice that the intermediate species formaldehyde and formic species are formed in small amounts, disappearing later when CO 2 reaches its maximum level. Regarding the chemical species detected, one can observe that the concentration of these chemical species always provides a carbon balance closure, near 100%, allowing one to


Introduction
Methanol is a toxic alcohol and a major volatile organic compound (VOC). It has been listed, since 1990, by the Environmental Protection Agency (EPA), as a hazardous air pollutant (HAPs) [1]. Methanol is primarily used as a chemical and solvent for industrial production, as well as an alternative fuel source for automobiles [2]. Methanol is mostly emitted from industrial solvent utilization facilities. This constitutes approximately 34% of all the emission sources from industry. Methanol has a high toxicity for humans [3]. It is readily absorbed into the body through inhalation, ingestion, and skin contact, and can cause blindness, headache, and nausea [4]. Moreover, large methanol doses may cause unconsciousness, coma and possible death due to respiratory failure [5]. In addition, the oxidation products of methanol, such as formaldehyde and formic acid, are carcinogenic to humans [6]. Consequently, the removal of methanol and its oxidation derivatives is critical to control air quality, in the industrial settings where there is frequent usage of these chemicals.
In recent years, photocatalysis has been shown to be one of the most efficient oxidation processes for the mineralization of numerous organic pollutants, especially those designated as VOCs [7][8][9]. Photocatalysis is considered to be a simple, sustainable technology, which can be successfully applied to the degradation of air pollutants at room temperature, with a modest energy requirement [10]. Regarding possible photocatalysts, titanium dioxide (TiO 2 ) is the most promising semiconductor, given that it can be widely used for air purification applications, and given that it is highly chemically stable, inexpensive, and safe for use by humans [11].
However, the demonstrated activity of current photocatalysts, as shown via quantum yields (QYs) is still limited. This is given the properties of available semiconductors such as rapid charge recombination, low surface area, and high band gap (3.20 eV) [9]. To circumvent this, research is currently being conducted to develop a mesoporous TiO 2 photocatalyst [12,13] which can be used with near-ultraviolet (near-UV) light for wastewater treatment [14][15][16][17][18]. Nevertheless, these materials have not been investigated thoroughly for air treatment in the context of reaction engineering principles [19]. In particular, there is no information in the current open technical literature that we are aware of, about QYs for VOCs degradation under visible light.
TiO 2 property modification have been achieved by doping/co-doping metals and nonmetals in a TiO 2 crystal lattice [20]. Among all metals and non-metals, silver and nitrogen doping into a TiO 2 crystal lattice has shown great promise for visible light photocatalytic activity [14,21]. In this respect, silver doping narrows the band gap energy as shown via surface plasmon resonance (SPR). Also, silver can act as an electron sink to store electrons (e − ) on a TiO 2 surface, thus reducing electron availability and/or delaying electron (e − ) and hole (h + ) recombination. In addition, incorporating nitrogen into a TiO 2 lattice has been shown to reduce the band gap energy by creating a new-mid band above the valence band. Furthermore, as reported recently by Sirivallop et al., (2020). the co-doping of silver and nitrogen in TiO 2 creates a synergistic effect, leading to enhanced photocatalytic activity under visible light [13].
It should be mentioned that the Photo-CREC-Air Reactor designed by the CREC (Chemical Reactor Engineering Centre), at the University of Western Ontario, Canada, offers special features for VOCs conversion. In this respect, Garcia-Hernandez et al. [22] and Lugo-Vega et al. [15] achieved the complete photoconversion of several volatile organic pollutants (such as acetone, acetaldehyde and formaldehyde) using a Degussa P25 photocatalyst under near-UV light, in the Photo-CREC-Air Reactor. This was achieved with very high QYs surpassing the 100% level.
Nevertheless, there is still a need to investigate VOCs conversion in a Photo-CREC-Air unit and to establish QYs using semiconductors which are active under visible light. Despite of its great importance, this significant topic remains unaddressed in the open technical literature [10]. The present research highlights the value of reducing VOCs in indoor spaces by using solar light, free of any energy expense, together with a photocatalyst. To accomplish this, in the present study, the photocatalytic conversion of a surrogate VOC species (methanol) using a mesoporous 5.6 at% N/Ag in TiO 2 is reported [13]. The valuable results obtained show that significant methanol conversions with high QYs can be achieved in a Photo-CREC-Air unit using the mesoporous N/Ag/TiO 2 photocatalyst.

Photocatalytic Mechanism of Methanol
The photocatalytic reaction mechanism of methanol can be envisioned as reported by de Lasa et al. [19] as a series of steps leading to the formation of hydroxyl (OH • ) radicals as follows: Step. 1 Photons with the adequate energy induce the formation of an electron and a positive hole (h + ): Step. 2 The hydroxyl radicals (OH • ) are formed as follows: ( (7) Thus, this leads to an overall stoichiometry to produce OH • as proposed as in Equation (8): (8) Step. 3 In the case of organic species in water, methanol (CH 3 OH) is progressively oxidized via a sequence of steps ending with the formation of CO 2 as follows: As a result, and assuming complete methanol conversion into CO 2 , and adding Equations (9)- (12) gives the following equation: Thus, and because of the postulated reaction mechanism, one can conclude that: (a) the photocatalytic reaction, as described via Equations (1)- (7), leads to an overall stoichiometry where 3 photons form 4 OH • groups (de Lasa et al. [19]) and (b) the complete methanol conversion into CO 2 requires 6 OH • groups to be consumed per every CO 2 molecule formed.

Properties of the Prepared Photocatalysts
The synthesized titanium dioxide-nitrogen-silver (N/Ag/TiO 2 ) photocatalyst and the bare-TiO 2 were characterized as reported in Table 1. It was found that the bare-TiO 2 has a surface area and pore volume of only 11.6 m 2 ·g −1 and 0.02 cm 3 ·g −1 , respectively. However, given that the N/Ag/TiO 2 photocatalyst has a mesoporous character, the surface area and pore diameter significantly increased to 101.3 m 2 ·g −1 and 0.26 cm 3 ·g −1 , respectively. These two parameters were around 10 times larger than those of bare-TiO 2 . This seems to be caused by the N and Ag species influence on the TiO 2 crystal lattice as further described in Appendix D.
The crystal structure and the crystallite sizes of the photocatalysts were investigated using the XRD spectra (JCPDS card No. 21-1272) for anatase (101) bare-TiO 2 [26], as shown in Figure 1a. This showed that the N/Ag/TiO 2 photocatalyst is composed of an anatase crystal phase like that of the mesoporous bare-TiO 2 [27,28]. For additional XRD results for the N/Ag/TiO 2, refer to Sirivallop et al. [13]. The crystallite sizes of the anatase (101) bare-TiO 2 were calculated using the Debye-Scherrer's formula (see Equation (14)) [29][30][31]. This showed that the N/Ag/TiO 2 powder involves 11.4 nm crystallites which are smaller than the 61.4 nm crystallites of the bare-TiO 2 ( Table 1). The smaller crystallite size of the N/Ag/TiO 2 is assumed to be caused by the influence of the N and Ag species doping under the solvothermal conditions, which limit the anatase crystal grain growth. This is in agreement with Yang et al. [32] and others, concluding that the anatase crystal size can be controlled by incorporating metals via the solvothermal method [16,[33][34][35]. In addition, one can also observe that the grain size reduction justifies the enhanced N/Ag/TiO 2 specific surface area. Furthermore, the change in the crystallite volume as well as the change in the density of a unit cell can be attributed to the influence of N and Ag loadings on the bare photocatalyst [36]. However, one can note that the increase in external agglomerate specific surface (Table 1) of the N/Ag/TiO 2 , as compared with the bare-TiO 2 , can have a negative effect on the photocatalytic reaction as observed later in this study, under near-UV and claimed by others [37]. a Crystallite size calculated from the X-ray diffraction (XRD) peak at 2θ of 25 • (101) using Debye-Scherrer's Equation. b Average agglomerate crystallite size calculated using scanning electron microscopy (SEM). c Unit cell density (ρ p ) calculated from the mass per unit cell over its cell volume [23,24]. d Agglomerate particle density = ρ crystallite (1 − ε), with ε being 0.5 for bare-TiO 2 and 0.6 for N/Ag/TiO 2 [25]. e Specific surface area (S BET ), pore volume (V p ) and pore diameter (D p ), determined by N 2 adsorption-desorption, using the Brunauer-Emmett-Teller (BET) and Barrett-Joyner-Halenda (BJH) methods, respectively. a Crystallite size calculated from the X-ray diffraction (XRD) peak at 2θ of 25° (101) using Debye-Scherrer's Equation. b Average agglomerate crystallite size calculated using scanning electron microscopy (SEM). c Unit cell density (ρp) calculated from the mass per unit cell over its cell volume [23,24]. d Agglomerate particle density = ρcrystallite (1 − ε), with ε being 0.5 for bare-TiO2 and 0.6 for N/Ag/TiO2 [25]. e Specific surface area (SBET), pore volume (Vp) and pore diameter (Dp), determined by N2 adsorption-desorption, using the Brunauer-Emmett-Teller (BET) and Barrett-Joyner-Halenda (BJH) methods, respectively.
The crystal structure and the crystallite sizes of the photocatalysts were investigated using the XRD spectra (JCPDS card No. 21-1272) for anatase (101) bare-TiO2 [26], as shown in Figure 1a. This showed that the N/Ag/TiO2 photocatalyst is composed of an anatase crystal phase like that of the mesoporous bare-TiO2 [27,28]. For additional XRD results for the N/Ag/TiO2, refer to Sirivallop et al. [13]. The crystallite sizes of the anatase (101) bare-TiO2 were calculated using the Debye-Scherrer's formula (see Equation (14)) [29][30][31]. This showed that the N/Ag/TiO2 powder involves 11.4 nm crystallites which are smaller than the 61.4 nm crystallites of the bare-TiO2 (Table 1). The smaller crystallite size of the N/Ag/TiO2 is assumed to be caused by the influence of the N and Ag species doping under the solvothermal conditions, which limit the anatase crystal grain growth. This is in agreement with Yang et al. [32] and others, concluding that the anatase crystal size can be controlled by incorporating metals via the solvothermal method [16,[33][34][35]. In addition, one can also observe that the grain size reduction justifies the enhanced N/Ag/TiO2 specific surface area. Furthermore, the change in the crystallite volume as well as the change in the density of a unit cell can be attributed to the influence of N and Ag loadings on the bare photocatalyst [36]. However, one can note that the increase in external agglomerate specific surface (Table 1) of the N/Ag/TiO2, as compared with the bare-TiO2, can have a negative effect on the photocatalytic reaction as observed later in this study, under near-UV and claimed by others [37]. Figure 1b displays the ultraviolet-visible (UV-vis) absorbance spectra for a N/Ag/TiO 2 and a bare-TiO 2 . It was observed that there was a significant change on the typical bare-TiO 2 absorbance variation with wavelength as follows (a) absorbance decreased as expected, in the 300-400 nm range, (b) absorbance augmented in 400 to 550 nm range. This modification was attributed to the surface plasmon resonance (SPR) effect of Ag nanoparticles [38][39][40][41][42][43] which was confirmed via photoluminescence (PL), as documented in the Supplementary Materials ( Figure S5) and by Sirivallop et al. [13]. Thus, it can be anticipated that photoexcited electrons and holes in the N/Ag/TiO 2 can be separated when using visible light more efficiently [44]. Another factor contributing to the anticipated visible light enhanced photoactivity was assigned to reduced band gaps for the N/Ag/TiO 2 as documented by others [13]. The photocatalyst surface acidity is also an important parameter for photocatalytic activity. This was determined by using the ammonia temperature-programmed desorption (TPD) under standard temperature and pressure (STP) conditions. Figure 2 reports the NH 3 -TPD profiles of both bare-TiO 2 and N/Ag/TiO 2 photocatalysts. Table 2 reports the amounts of NH 3 desorbed from the studied photocatalyst, obtained by the integration of TPD profiles. One can see that N/Ag/TiO 2 exhibited the higher peak intensity and higher total amount of NH 3 desorbed per unit mass, as compared to the bare-TiO 2 . However as shown in Table 1, and once the desorbed amount of NH 3 based on the unit area of semiconductor is considered, one can see that the bare-TiO 2 displays larger ammonia desorbed values than the N/Ag/TiO 2 . This clearly indicates that the overall N/Ag/TiO 2 acidity density per unit surface area is significantly reduced due to the N and Ag addition. mented in the Supplementary Materials ( Figure S5) and by Sirivallop et al., [13]. Thus, it can be anticipated that photoexcited electrons and holes in the N/Ag/TiO2 can be separated when using visible light more efficiently [44]. Another factor contributing to the anticipated visible light enhanced photoactivity was assigned to reduced band gaps for the N/Ag/TiO2 as documented by others [13].
The photocatalyst surface acidity is also an important parameter for photocatalytic activity. This was determined by using the ammonia temperature-programmed desorption (TPD) under standard temperature and pressure (STP) conditions. Figure 2 reports the NH3-TPD profiles of both bare-TiO2 and N/Ag/TiO2 photocatalysts. Table 2 reports the amounts of NH3 desorbed from the studied photocatalyst, obtained by the integration of TPD profiles. One can see that N/Ag/TiO2 exhibited the higher peak intensity and higher total amount of NH3 desorbed per unit mass, as compared to the bare-TiO2. However as shown in Table 1, and once the desorbed amount of NH3 based on the unit area of semiconductor is considered, one can see that the bare-TiO2 displays larger ammonia desorbed values than the N/Ag/TiO2. This clearly indicates that the overall N/Ag/TiO2 acidity density per unit surface area is significantly reduced due to the N and Ag addition.  Furthermore, an X-ray photoelectron spectroscopy (XPS) analysis was performed to determine the semiconductor surface composition and to understand how the N and Ag  Furthermore, an X-ray photoelectron spectroscopy (XPS) analysis was performed to determine the semiconductor surface composition and to understand how the N and Ag dopants interact with the bare-TiO 2 lattice. Additional XPS information regarding the photocatalyst of the present study is given in Sirivallop et al. [13]. The surface compositions and chemical states of the prepared photocatalysts of bare-TiO 2 and N/Ag/TiO 2 are summarized in Table 3. Figure 3a shows the survey XPS spectra of both the N/Ag/TiO 2 and the bare-TiO 2 . One can notice that the characteristic peaks of Ti 2p and O 1s, located at the binding energies (BE) of around 458-465 eV and 530 eV, respectively, were observed in both the bare-TiO 2 and the N/Ag/TiO 2 sample. This was attributed to the Ti-O-Ti bonds in the bare-TiO 2 . However, the additional peaks of the nitrogen atom as well those of the silver atom were only observed in the N/Ag/TiO 2 sample, at about 400 eV and 370 eV for N 1s and Ag 3d, respectively. The XPS shows the 284.6 eV C 1s the carbon atom reference peak as well. dopants interact with the bare-TiO2 lattice. Additional XPS information regarding the photocatalyst of the present study is given in Sirivallop et al., [13]. The surface compositions and chemical states of the prepared photocatalysts of bare-TiO2 and N/Ag/TiO2 are summarized in Table 3. Figure 3a shows the survey XPS spectra of both the N/Ag/TiO2 and the bare-TiO2. One can notice that the characteristic peaks of Ti 2p and O 1s, located at the binding energies (BE) of around 458-465 eV and 530 eV, respectively, were observed in both the bare-TiO2 and the N/Ag/TiO2 sample. This was attributed to the Ti-O-Ti bonds in the bare-TiO2. However, the additional peaks of the nitrogen atom as well those of the silver atom were only observed in the N/Ag/TiO2 sample, at about 400 eV and 370 eV for N 1s and Ag 3d, respectively. The XPS shows the 284.6 eV C 1s the carbon atom reference peak as well.  Figure 3. (a) Full X-ray photoelectron spectroscopy (XPS) spectra of N/Ag/TiO2 and bare-TiO2 photocatalysts and high-resolution spectra of (b) Ti 2p, (c) N 1s, and (d) Ag 3d. By considering the Ti state from the XPS high-resolution spectra as shown in Figure  3b, the intensive peak of Ti 2p3/2, at a binding energy of 458.5 eV (>90 at.%), corresponding to the Ti 4+ in the bare-TiO2 lattice, was observed. This was the case agreement with [45,46] for both the bare-TiO2 and N/Ag/TiO2 photocatalysts. Also, a small Ti2O3 amount (<10 By considering the Ti state from the XPS high-resolution spectra as shown in Figure 3b, the intensive peak of Ti 2p 3/2 , at a binding energy of 458.5 eV (>90 at.%), corresponding to the Ti 4+ in the bare-TiO 2 lattice, was observed. This was the case agreement with [45,46] for both the bare-TiO 2 and N/Ag/TiO 2 photocatalysts. Also, a small Ti 2 O 3 amount (<10 at.%), corresponding to the oxygen vacancies was also observed. One should note that the Ti 2p bands for the N/Ag/TiO 2 shifted slightly to the lower binding energies. This was attributed to the change in electronic interaction between bare-TiO 2 and silver [47]. Figure 3c shows the high-resolution XPS spectra for N1s, located in the 399-401.1 eV binding energy (BE) range. This suggests that the incorporation of an N atom into the bare-TiO 2 crystal lattice was achieved by the bonding of three different species. The XPS spectra bands at 398.1 eV and 399.7 eV correspond to interstitial N doping (33.97 at.%) and substitutional N doping (36.99 at.%), respectively [48]. The higher BE of 401.1 eV (29.04 at.%) is usually ascribed to a chemisorbed nitrogen [49]. The most intensive peaks of the substitutional N, which occur by replacing the O atom by an N atom, in the bare-TiO 2 lattice in order to form O-Ti-N linkages, as well as the interstitial N are much more effective in the bare-TiO 2 crystal lattice [45][46][47][48][49][50]. Due to the electronegativity of the O atom (3.5) is greater than that of the N atom (3.0), it affects electron transfers from the N atom to the Ti atom. This leads to a reduction in electron density on the N atom, and subsequently increases the electron density on the Ti atom [24]. The BE peak at about 399.9 eV is possibly related to a reduction of nitrogen electron density due to the high electronegativity of oxygen, as reported by others [50][51][52]. Consequently, this further proves that N was incorporated into the lattice and substituted for oxygen. Figure 3d depicts the XPS spectra for Ag 3d with two major peaks of Ag 3d 3/2 and Ag 3d 5/2 , located at 373.60 eV and 367.6 eV, respectively. Considering the signal peak of Ag 3d 5/2 , it was noticed that the introduction of silver in the lattice surface of the bare-TiO 2 provides three different silver states: Ag 0 (5.36 at.%), Ag 2 O (83.93 at.%) and AgO (10.71 at.%) located at 369.8 eV, 368.4 eV and 367.8 eV, respectively [47]. This showed that the content of oxidized silver in the bare-TiO 2 is larger than the content of metallic silver (Ag 0 ), with both Ag 0 and Ag + in the bare-TiO 2 crystal lattice, playing a critical role in the electron-hole separation and as a result, the photocatalytic performance [53,54]. According to Santos et al. (2015), Ag 0 clusters could allow strong visible light absorption on the TiO 2 surface [55]. This is due to their surface plasmon resonance (SPR) effect. Furthermore, Batalović et al. (2017) have mentioned that a metal atom deposited on a TiO 2 surface could create a catalytically active surface, for reaction intermediates [45].
In this respect, as seen in previous studies, and another paper by Sirivallop et al. [13], the N and Ag addition in bare-TiO 2 was responsible for several positive effects on the physicochemical properties such as: (a) smaller anatase crystallites, (b) higher surface area, (c) surface plasmon resonance (SPR) for silver, (d) narrow bandgap energy and (e) high charge separation efficiency. One should note, however, that the increased of external agglomerate specific surface as well as the reduced acidity based on the unit surface area, was observed in the case of the N/Ag/TiO 2 crystal lattice. This combination of semiconductor properties allows one to explain the methanol photocatalytic degradation under visible and near-UV irradiation.

Photon Absorption Efficiency
The measurements of incident radiation, transmitted light and backscattered light by the photocatalyst were taken at various axial and angular positions, in order to obtain the total photon absorption by the photocatalyst. Table 4 reports the total photon absorption calculated, based on the macroscopic radiation balances of the bare-TiO 2 and of the N/Ag/TiO 2 -coated photocatalyst on the cylindrical stainless-steel woven mesh (2 wt.% loadings), under either near-UV or visible light illumination. The total photons transmitted and backscattered by the photocatalyst were also determined by showing that the incident light was not only absorbed by the photocatalyst but could also be transmitted and backscattered from the mesh surface. Figure 4 reports the photon absorption efficiency of near-UV light and visible light irradiation calculated from the ratio of absorbed photons by the photocatalyst over the irradiated photons reaching the photocatalyst surface. Table 4. Calculated photon fluxes of incident light (P i , r = 5.9 cm), transmitted light (P t , 5.25 cm) and backscattered light (P bs , r = 7.7) by the coated mesh. All occur when using the woven mesh coated with 2 wt.% of photocatalyst loading under either near-UV (320-380 nm wavelength) or visible light (380-700 nm wavelength). that the incident light was not only absorbed by the photocatalyst but could also be transmitted and backscattered from the mesh surface.    In this respect, one can see in Figure 4 that the N/Ag/TiO2 exhibits higher photon absorption efficiencies both under near-UV (80-90%) as well as visible light (70-80%). On the other hand, the bare-TiO2 showed a 65-80% photon absorption efficiency under near-UV irradiation, with a poor absorption capacity (less than 30%) under the visible light radiation. Furthermore, it was also noticed in Figure 4b (using the N/Ag/TiO2), that the photon absorption efficiency increased with the amount of photocatalyst loading on the stainless-steel woven mesh, with 2 wt.% providing the highest photon absorption. Given this demonstrated higher photon absorption, these results anticipate that the N/Ag/TiO2 photocatalyst holds special promise, for the photocatalytic degradation of VOCs under visible light. In this respect, one can see in Figure 4 that the N/Ag/TiO 2 exhibits higher photon absorption efficiencies both under near-UV (80-90%) as well as visible light (70-80%). On the other hand, the bare-TiO 2 showed a 65-80% photon absorption efficiency under near-UV irradiation, with a poor absorption capacity (less than 30%) under the visible light radiation. Furthermore, it was also noticed in Figure 4b (using the N/Ag/TiO 2 ), that the photon absorption efficiency increased with the amount of photocatalyst loading on the stainless-steel woven mesh, with 2 wt.% providing the highest photon absorption. Given this demonstrated higher photon absorption, these results anticipate that the N/Ag/TiO 2 photocatalyst holds special promise, for the photocatalytic degradation of VOCs under visible light. The photocatalytic oxidation of gas phase methanol in a recirculating batch Photo-CREC-Air Reactor was carried out under two different light source illuminations: near-UV and visible light, by using either bare-TiO 2 or N/Ag/TiO 2 coated on a stainless-steel woven mesh. Various chemical species formed were determined by using a gas chromatograph unit with a flame ionization detector (GC-FID). Supplementary Materials A and B reports a typical GC-FID chromatogram and calibration curves for various photocatalytic methanol conversion products. This chromatogram showed conclusively that there are no other chemical species detected under dark conditions, except the injected methanol and the CO 2 contained in the atmosphere at a constant concentration. Figure 5a,b report the photocatalytic conversion of methanol and the formation of formaldehyde and formic acid intermediates, when using the bare-TiO 2 under near-UV and visible light, respectively. The coated bare-TiO 2 in Figure 5a shows an excellent photocatalytic activity under the near-UV light irradiation, with rapid methanol degradation and essentially zero methanol concentration achieved in 110 min of irradiation time. One can also notice that the intermediate species formaldehyde and formic species are formed in small amounts, disappearing later when CO 2 reaches its maximum level. Regarding the chemical species detected, one can observe that the concentration of these chemical species always provides a carbon balance closure, near 100%, allowing one to conclude that there is a modest influence of adsorbed hydrocarbon species during the run. One can also see in Figure 5b, and in contrast with the results in Figure 5a, that the bare-TiO 2 photocatalyst becomes essentially inactive under the visible light, with methanol concentration hardly decreasing with irradiation time. One should note that the close to 100% carbon balance shows the reliable accounting of all carbon containing species during the experiments.

Light
to-CREC-Air Reactor was carried out under two different light source illuminations: near-UV and visible light, by using either bare-TiO2 or N/Ag/TiO2 coated on a stainless-steel woven mesh. Various chemical species formed were determined by using a gas chromatograph unit with a flame ionization detector (GC-FID). Supplementary Materials A and B reports a typical GC-FID chromatogram and calibration curves for various photocatalytic methanol conversion products. This chromatogram showed conclusively that there are no other chemical species detected under dark conditions, except the injected methanol and the CO2 contained in the atmosphere at a constant concentration. Figure 5a,b report the photocatalytic conversion of methanol and the formation of formaldehyde and formic acid intermediates, when using the bare-TiO2 under near-UV and visible light, respectively. The coated bare-TiO2 in Figure 5a shows an excellent photocatalytic activity under the near-UV light irradiation, with rapid methanol degradation and essentially zero methanol concentration achieved in 110 min of irradiation time. One can also notice that the intermediate species formaldehyde and formic species are formed in small amounts, disappearing later when CO2 reaches its maximum level. Regarding the chemical species detected, one can observe that the concentration of these chemical species always provides a carbon balance closure, near 100%, allowing one to conclude that there is a modest influence of adsorbed hydrocarbon species during the run. One can also see in Figure 5b, and in contrast with the results in Figure 5a, that the bare-TiO2 photocatalyst becomes essentially inactive under the visible light, with methanol concentration hardly decreasing with irradiation time. One should note that the close to 100% carbon balance shows the reliable accounting of all carbon containing species during the experiments.  , and the right Y red coordinate refers to intermediates concentration of formaldehyde (˟) and formic acid ( ) species; in addition to, (ii) Mean values corresponding to at least 3 repeats with a standard deviation (SD) of 10 ± 3%. Note2: The close to 100% total carbon balance shows the reliable accounting of all carbon-containing species during the runs. Figure 6a,b report the photocatalytic conversions of methanol under near-UV and visible light, using the N/Ag/TiO2 photocatalyst, which displays good photodegradation in both cases. Figure 6a,b also show that both formaldehyde and formic acid are two to-CREC-Air Reactor was carried out under two different light source illuminations: near-UV and visible light, by using either bare-TiO2 or N/Ag/TiO2 coated on a stainless-steel woven mesh. Various chemical species formed were determined by using a gas chromatograph unit with a flame ionization detector (GC-FID). Supplementary Materials A and B reports a typical GC-FID chromatogram and calibration curves for various photocatalytic methanol conversion products. This chromatogram showed conclusively that there are no other chemical species detected under dark conditions, except the injected methanol and the CO2 contained in the atmosphere at a constant concentration. Figure 5a,b report the photocatalytic conversion of methanol and the formation of formaldehyde and formic acid intermediates, when using the bare-TiO2 under near-UV and visible light, respectively. The coated bare-TiO2 in Figure 5a shows an excellent photocatalytic activity under the near-UV light irradiation, with rapid methanol degradation and essentially zero methanol concentration achieved in 110 min of irradiation time. One can also notice that the intermediate species formaldehyde and formic species are formed in small amounts, disappearing later when CO2 reaches its maximum level. Regarding the chemical species detected, one can observe that the concentration of these chemical species always provides a carbon balance closure, near 100%, allowing one to conclude that there is a modest influence of adsorbed hydrocarbon species during the run. One can also see in Figure 5b, and in contrast with the results in Figure 5a, that the bare-TiO2 photocatalyst becomes essentially inactive under the visible light, with methanol concentration hardly decreasing with irradiation time. One should note that the close to 100% carbon balance shows the reliable accounting of all carbon containing species during the experiments.  ) as well as total carbon ( ○ ), and the right Y red coordinate refers to intermediates concentration of formaldehyde ( ˟ ) and formic acid ( ) species; in addition to, (ii) Mean values corresponding to at least 3 repeats with a standard deviation (SD) of 10 ± 3%. Note2: The close to 100% total carbon balance shows the reliable accounting of all carbon-containing species during the runs. Figure 6a,b report the photocatalytic conversions of methanol under near-UV and visible light, using the N/Ag/TiO2 photocatalyst, which displays good photodegradation in both cases. Figure 6a,b also show that both formaldehyde and formic acid are two ), CO 2 ( to-CREC-Air Reactor was carried out under two different light source illuminations: near-UV and visible light, by using either bare-TiO2 or N/Ag/TiO2 coated on a stainless-steel woven mesh. Various chemical species formed were determined by using a gas chromatograph unit with a flame ionization detector (GC-FID). Supplementary Materials A and B reports a typical GC-FID chromatogram and calibration curves for various photocatalytic methanol conversion products. This chromatogram showed conclusively that there are no other chemical species detected under dark conditions, except the injected methanol and the CO2 contained in the atmosphere at a constant concentration. Figure 5a,b report the photocatalytic conversion of methanol and the formation of formaldehyde and formic acid intermediates, when using the bare-TiO2 under near-UV and visible light, respectively. The coated bare-TiO2 in Figure 5a shows an excellent photocatalytic activity under the near-UV light irradiation, with rapid methanol degradation and essentially zero methanol concentration achieved in 110 min of irradiation time. One can also notice that the intermediate species formaldehyde and formic species are formed in small amounts, disappearing later when CO2 reaches its maximum level. Regarding the chemical species detected, one can observe that the concentration of these chemical species always provides a carbon balance closure, near 100%, allowing one to conclude that there is a modest influence of adsorbed hydrocarbon species during the run. One can also see in Figure 5b, and in contrast with the results in Figure 5a, that the bare-TiO2 photocatalyst becomes essentially inactive under the visible light, with methanol concentration hardly decreasing with irradiation time. One should note that the close to 100% carbon balance shows the reliable accounting of all carbon containing species during the experiments.  ) as well as total carbon ( ○ ), and the right Y red coordinate refers to intermediates concentration of formaldehyde ( ˟ ) and formic acid ( ) species; in addition to, (ii) Mean values corresponding to at least 3 repeats with a standard deviation (SD) of 10 ± 3%. Note2: The close to 100% total carbon balance shows the reliable accounting of all carbon-containing species during the runs. Figure 6a,b report the photocatalytic conversions of methanol under near-UV and visible light, using the N/Ag/TiO2 photocatalyst, which displays good photodegradation in both cases. Figure 6a,b also show that both formaldehyde and formic acid are two ) as well as total carbon ( to-CREC-Air Reactor was carried out under two different light source illuminations: near-UV and visible light, by using either bare-TiO2 or N/Ag/TiO2 coated on a stainless-steel woven mesh. Various chemical species formed were determined by using a gas chromatograph unit with a flame ionization detector (GC-FID). Supplementary Materials A and B reports a typical GC-FID chromatogram and calibration curves for various photocatalytic methanol conversion products. This chromatogram showed conclusively that there are no other chemical species detected under dark conditions, except the injected methanol and the CO2 contained in the atmosphere at a constant concentration. Figure 5a,b report the photocatalytic conversion of methanol and the formation of formaldehyde and formic acid intermediates, when using the bare-TiO2 under near-UV and visible light, respectively. The coated bare-TiO2 in Figure 5a shows an excellent photocatalytic activity under the near-UV light irradiation, with rapid methanol degradation and essentially zero methanol concentration achieved in 110 min of irradiation time. One can also notice that the intermediate species formaldehyde and formic species are formed in small amounts, disappearing later when CO2 reaches its maximum level. Regarding the chemical species detected, one can observe that the concentration of these chemical species always provides a carbon balance closure, near 100%, allowing one to conclude that there is a modest influence of adsorbed hydrocarbon species during the run. One can also see in Figure 5b, and in contrast with the results in Figure 5a, that the bare-TiO2 photocatalyst becomes essentially inactive under the visible light, with methanol concentration hardly decreasing with irradiation time. One should note that the close to 100% carbon balance shows the reliable accounting of all carbon containing species during the experiments.  ) as well as total carbon ( ○ ), and the right Y red coordinate refers to intermediates concentration of formaldehyde ( ˟ ) and formic acid ( ) species; in addition to, (ii) Mean values corresponding to at least 3 repeats with a standard deviation (SD) of 10 ± 3%. Note2: The close to 100% total carbon balance shows the reliable accounting of all carbon-containing species during the runs. Figure 6a,b report the photocatalytic conversions of methanol under near-UV and visible light, using the N/Ag/TiO2 photocatalyst, which displays good photodegradation in both cases. Figure 6a,b also show that both formaldehyde and formic acid are two ), and the right Y red coordinate refers to intermediates concentration of formaldehyde ( The photocatalytic oxidation of gas phase methanol in a recirculating batch Pho-to-CREC-Air Reactor was carried out under two different light source illuminations: near-UV and visible light, by using either bare-TiO2 or N/Ag/TiO2 coated on a stainless-steel woven mesh. Various chemical species formed were determined by using a gas chromatograph unit with a flame ionization detector (GC-FID). Supplementary Materials A and B reports a typical GC-FID chromatogram and calibration curves for various photocatalytic methanol conversion products. This chromatogram showed conclusively that there are no other chemical species detected under dark conditions, except the injected methanol and the CO2 contained in the atmosphere at a constant concentration. Figure 5a,b report the photocatalytic conversion of methanol and the formation of formaldehyde and formic acid intermediates, when using the bare-TiO2 under near-UV and visible light, respectively. The coated bare-TiO2 in Figure 5a shows an excellent photocatalytic activity under the near-UV light irradiation, with rapid methanol degradation and essentially zero methanol concentration achieved in 110 min of irradiation time. One can also notice that the intermediate species formaldehyde and formic species are formed in small amounts, disappearing later when CO2 reaches its maximum level. Regarding the chemical species detected, one can observe that the concentration of these chemical species always provides a carbon balance closure, near 100%, allowing one to conclude that there is a modest influence of adsorbed hydrocarbon species during the run. One can also see in Figure 5b, and in contrast with the results in Figure 5a, that the bare-TiO2 photocatalyst becomes essentially inactive under the visible light, with methanol concentration hardly decreasing with irradiation time. One should note that the close to 100% carbon balance shows the reliable accounting of all carbon containing species during the experiments.  ) as well as total carbon ( ○ ), and the right Y red coordinate refers to intermediates concentration of formaldehyde ( ˟ ) and formic acid ( ) species; in addition to, (ii) Mean values corresponding to at least 3 repeats with a standard deviation (SD) of 10 ± 3%. Note2: The close to 100% total carbon balance shows the reliable accounting of all carbon-containing species during the runs. Figure 6a,b report the photocatalytic conversions of methanol under near-UV and visible light, using the N/Ag/TiO2 photocatalyst, which displays good photodegradation in both cases. Figure 6a,b also show that both formaldehyde and formic acid are two ) and formic acid ( to-CREC-Air Reactor was carried out under two different light source illuminations: near-UV and visible light, by using either bare-TiO2 or N/Ag/TiO2 coated on a stainless-steel woven mesh. Various chemical species formed were determined by using a gas chromatograph unit with a flame ionization detector (GC-FID). Supplementary Materials A and B reports a typical GC-FID chromatogram and calibration curves for various photocatalytic methanol conversion products. This chromatogram showed conclusively that there are no other chemical species detected under dark conditions, except the injected methanol and the CO2 contained in the atmosphere at a constant concentration. Figure 5a,b report the photocatalytic conversion of methanol and the formation of formaldehyde and formic acid intermediates, when using the bare-TiO2 under near-UV and visible light, respectively. The coated bare-TiO2 in Figure 5a shows an excellent photocatalytic activity under the near-UV light irradiation, with rapid methanol degradation and essentially zero methanol concentration achieved in 110 min of irradiation time. One can also notice that the intermediate species formaldehyde and formic species are formed in small amounts, disappearing later when CO2 reaches its maximum level. Regarding the chemical species detected, one can observe that the concentration of these chemical species always provides a carbon balance closure, near 100%, allowing one to conclude that there is a modest influence of adsorbed hydrocarbon species during the run. One can also see in Figure 5b, and in contrast with the results in Figure 5a, that the bare-TiO2 photocatalyst becomes essentially inactive under the visible light, with methanol concentration hardly decreasing with irradiation time. One should note that the close to 100% carbon balance shows the reliable accounting of all carbon containing species during the experiments.  ) as well as total carbon ( ○ ), and the right Y red coordinate refers to intermediates concentration of formaldehyde ( ˟ ) and formic acid ( ) species; in addition to, (ii) Mean values corresponding to at least 3 repeats with a standard deviation (SD) of 10 ± 3%. Note2: The close to 100% total carbon balance shows the reliable accounting of all carbon-containing species during the runs. Figure 6a,b report the photocatalytic conversions of methanol under near-UV and visible light, using the N/Ag/TiO2 photocatalyst, which displays good photodegradation in both cases. Figure 6a,b also show that both formaldehyde and formic acid are two ) species; in addition to, (ii) Mean values corresponding to at least 3 repeats with a standard deviation (SD) of 10 ± 3%. Note2: The close to 100% total carbon balance shows the reliable accounting of all carbon-containing species during the runs. Figure 6a,b report the photocatalytic conversions of methanol under near-UV and visible light, using the N/Ag/TiO 2 photocatalyst, which displays good photodegradation in both cases. Figure 6a,b also show that both formaldehyde and formic acid are two produced intermediate species in both cases, while concentrations are reduced with irradiation time. Note 2: One should note that close to 100% total carbon, calculated as a summation of all carbon-containing species at any time during the run, shows the reliable accounting of all chemical species.
Results obtained during the developed runs, as shown in Figure 6a,b, can be explained as follows: (a) there is essentially no detectable photocatalytic activity for the bare-TiO 2 and (b) there is significant photocatalytic activity when using N/Ag/TiO 2 photocatalysts. Differences in photoactivity can be assigned to the reduction of the optical band gap, and the enhanced photon absorption capacity of the N/Ag/TiO 2 [45,55].
From the above experimental results, a series-parallel reaction pathway for the photocatalytic conversion of gas-phase methanol to CO 2 , in a Photo-CREC-Air Reactor, can be considered, as described in Figure 7. produced intermediate species in both cases, while concentrations are reduced with irradiation time. Note 2: One should note that close to 100% total carbon, calculated as a summation of all carbon-containing species at any time during the run, shows the reliable accounting of all chemical species. Results obtained during the developed runs, as shown in Figure 6a,b, can be explained as follows: (a) there is essentially no detectable photocatalytic activity for the bare-TiO2 and (b) there is significant photocatalytic activity when using N/Ag/TiO2 photocatalysts. Differences in photoactivity can be assigned to the reduction of the optical band gap, and the enhanced photon absorption capacity of the N/Ag/TiO2 [45,55].
From the above experimental results, a series-parallel reaction pathway for the photocatalytic conversion of gas-phase methanol to CO2, in a Photo-CREC-Air Reactor, can be considered, as described in Figure 7. This series-parallel network accounts for the following steps: (i) a first reaction step (R1), with methanol oxidizing to CO2 directly, without any detectable reaction intermediates, (ii) a second reaction step (R2) with methanol oxidizing to CO2, yielding formal- conclude that there is a modest influence of adsorbed hydrocarbon species during the run. One can also see in Figure 5b, and in contrast with the results in Figure 5a, that the bare-TiO2 photocatalyst becomes essentially inactive under the visible light, with methanol concentration hardly decreasing with irradiation time. One should note that the close to 100% carbon balance shows the reliable accounting of all carbon containing species during the experiments.  ) as well as total carbon ( ○ ), and the right Y red coordinate refers to intermediates concentration of formaldehyde ( ˟ ) and formic acid ( ) species; in addition to, (ii) Mean values corresponding to at least 3 repeats with a standard deviation (SD) of 10 ± 3%. Note2: The close to 100% total carbon balance shows the reliable accounting of all carbon-containing species during the runs. Figure 6a,b report the photocatalytic conversions of methanol under near-UV and visible light, using the N/Ag/TiO2 photocatalyst, which displays good photodegradation in both cases. Figure 6a,b also show that both formaldehyde and formic acid are two ), CO 2 ( conclude that there is a modest influence of adsorbed hydrocarbon species during the run. One can also see in Figure 5b, and in contrast with the results in Figure 5a, that the bare-TiO2 photocatalyst becomes essentially inactive under the visible light, with methanol concentration hardly decreasing with irradiation time. One should note that the close to 100% carbon balance shows the reliable accounting of all carbon containing species during the experiments.  ) as well as total carbon ( ○ ), and the right Y red coordinate refers to intermediates concentration of formaldehyde ( ˟ ) and formic acid ( ) species; in addition to, (ii) Mean values corresponding to at least 3 repeats with a standard deviation (SD) of 10 ± 3%. Note2: The close to 100% total carbon balance shows the reliable accounting of all carbon-containing species during the runs. Figure 6a,b report the photocatalytic conversions of methanol under near-UV and visible light, using the N/Ag/TiO2 photocatalyst, which displays good photodegradation in both cases. Figure 6a,b also show that both formaldehyde and formic acid are two ) as well as total carbon ( conclude that there is a modest influence of adsorbed hydrocarbon species during the run. One can also see in Figure 5b, and in contrast with the results in Figure 5a, that the bare-TiO2 photocatalyst becomes essentially inactive under the visible light, with methanol concentration hardly decreasing with irradiation time. One should note that the close to 100% carbon balance shows the reliable accounting of all carbon containing species during the experiments.  ) as well as total carbon ( ○ ), and the right Y red coordinate refers to intermediates concentration of formaldehyde ( ˟ ) and formic acid ( ) species; in addition to, (ii) Mean values corresponding to at least 3 repeats with a standard deviation (SD) of 10 ± 3%. Note2: The close to 100% total carbon balance shows the reliable accounting of all carbon-containing species during the runs. Figure 6a,b report the photocatalytic conversions of methanol under near-UV and visible light, using the N/Ag/TiO2 photocatalyst, which displays good photodegradation in both cases. Figure 6a,b also show that both formaldehyde and formic acid are two ), and the right Y red coordinate refers to intermediates concentration of formaldehyde ( conclude that there is a modest influence of adsorbed hydrocarbon species during the run. One can also see in Figure 5b, and in contrast with the results in Figure 5a, that the bare-TiO2 photocatalyst becomes essentially inactive under the visible light, with methanol concentration hardly decreasing with irradiation time. One should note that the close to 100% carbon balance shows the reliable accounting of all carbon containing species during the experiments.  ) as well as total carbon ( ○ ), and the right Y red coordinate refers to intermediates concentration of formaldehyde ( ˟ ) and formic acid ( ) species; in addition to, (ii) Mean values corresponding to at least 3 repeats with a standard deviation (SD) of 10 ± 3%. Note2: The close to 100% total carbon balance shows the reliable accounting of all carbon-containing species during the runs. Figure 6a,b report the photocatalytic conversions of methanol under near-UV and visible light, using the N/Ag/TiO2 photocatalyst, which displays good photodegradation in both cases. Figure 6a,b also show that both formaldehyde and formic acid are two ) and formic acid ( conclude that there is a modest influence of adsorbed hydrocarbon species during the run. One can also see in Figure 5b, and in contrast with the results in Figure 5a, that the bare-TiO2 photocatalyst becomes essentially inactive under the visible light, with methanol concentration hardly decreasing with irradiation time. One should note that the close to 100% carbon balance shows the reliable accounting of all carbon containing species during the experiments.  ) as well as total carbon ( ○ ), and the right Y red coordinate refers to intermediates concentration of formaldehyde ( ˟ ) and formic acid ( ) species; in addition to, (ii) Mean values corresponding to at least 3 repeats with a standard deviation (SD) of 10 ± 3%. Note2: The close to 100% total carbon balance shows the reliable accounting of all carbon-containing species during the runs. Figure 6a,b report the photocatalytic conversions of methanol under near-UV and visible light, using the N/Ag/TiO2 photocatalyst, which displays good photodegradation in both cases. Figure 6a,b also show that both formaldehyde and formic acid are two ) species; in addition to, (ii) mean values corresponding to at least 3 repeats with a standard deviation (SD) of 15 ± 5%. Note 2: The close to 100% total carbon shows the reliable accounting of all carbon containing species during the runs. Results obtained during the developed runs, as shown in Figure 6a,b, can be explained as follows: (a) there is essentially no detectable photocatalytic activity for the bare-TiO2 and (b) there is significant photocatalytic activity when using N/Ag/TiO2 photocatalysts. Differences in photoactivity can be assigned to the reduction of the optical band gap, and the enhanced photon absorption capacity of the N/Ag/TiO2 [45,55].
From the above experimental results, a series-parallel reaction pathway for the photocatalytic conversion of gas-phase methanol to CO2, in a Photo-CREC-Air Reactor, can be considered, as described in Figure 7. This series-parallel network accounts for the following steps: (i) a first reaction step (R1), with methanol oxidizing to CO2 directly, without any detectable reaction intermediates, (ii) a second reaction step (R2) with methanol oxidizing to CO2, yielding formal- This series-parallel network accounts for the following steps: (i) a first reaction step (R 1 ), with methanol oxidizing to CO 2 directly, without any detectable reaction intermediates, (ii) a second reaction step (R 2 ) with methanol oxidizing to CO 2 , yielding formaldehyde (CH 2 O) as a detectable intermediate, and decomposing later into CO 2 , and (iii) a third reaction step (R 3 ), accounting for methanol oxidizing to CO 2 , with formaldehyde (CH 2 O) and formic acid (HCOOH) as intermediate species.
The series-parallel network mechanism can be considered on the basis of (a) methanol concentration decreasing progressively, with CO 2 continuously increasing with irradiation time, (b) a CO 2 formation rate of non-zero at early irradiation times and (c) formaldehyde and formic acid displaying maximum values at about similar irradiation times.
This photocatalytic pathway for methanol oxidation photoconversion is in agreement with Lv et al. [56], Lugo-Vega et al. [15], and de Lasa et al. [19]. de Lasa et al. (2005) introduced the "series-parallel" network scheme, validating it based on the expected and unavoidable differences in photon density at various photocatalytic reactor locations.

Effect of Photocatalyst Loading
The photocatalytic degradation of methanol was evaluated at a relative humidity of 35-46% range (refer to Appendix B), varying the percentage weight of the immobilized photocatalyst on the cylindrical stainless-steel woven mesh as follows: 0.5 wt.%, 1 wt.% and 2 wt.% Figure 8a,b report the photocatalytic activity of methanol degradation using different loadings of bare-TiO 2 and N/Ag/TiO 2 immobilized on the mesh, respectively. From these figures, one can notice that the activity of photocatalytic methanol degradation under near-UV light depends on the amount of photocatalyst loaded. Consistent with this, higher amounts (2 wt.%) of either bare-TiO 2 or N/Ag/TiO 2 showed greater methanol degradation rates as compared to lower photocatalyst loadings. For bare-TiO 2 , the fastest photocatalytic reaction for methanol degradation was observed when using a mesh coated with 2 wt.% of bare-TiO 2 . This showed a complete methanol degradation within 90 min of near-UV irradiation: k = 2.2 × 10 −2 min −1 (R 2 = 0.98) (see Table 5).
(2005) introduced the "series-parallel" network scheme, validating it based on the expected and unavoidable differences in photon density at various photocatalytic reactor locations.

Effect of Photocatalyst Loading
The photocatalytic degradation of methanol was evaluated at a relative humidity of 35-46% range (refer to Appendix B), varying the percentage weight of the immobilized photocatalyst on the cylindrical stainless-steel woven mesh as follows: 0.5 wt.%, 1 wt.% and 2 wt.% Figure 8a,b report the photocatalytic activity of methanol degradation using different loadings of bare-TiO2 and N/Ag/TiO2 immobilized on the mesh, respectively. From these figures, one can notice that the activity of photocatalytic methanol degradation under near-UV light depends on the amount of photocatalyst loaded. Consistent with this, higher amounts (2 wt.%) of either bare-TiO2 or N/Ag/TiO2 showed greater methanol degradation rates as compared to lower photocatalyst loadings. For bare-TiO2, the fastest photocatalytic reaction for methanol degradation was observed when using a mesh coated with 2 wt.% of bare-TiO2. This showed a complete methanol degradation within 90 min of near-UV irradiation: k = 2.2 × 10 −2 min −1 (R 2 = 0.98) (see Table 5).   Table 5 reports the photocatalytic performance of methanol degradation using the bare-TiO 2 and the N/Ag/TiO 2 and employing pseudo first-order reaction rates. Kinetic constants were also determined for each experimental condition, based on at least three repeats. Data obtained show higher kinetic constants at the higher photocatalyst loadings, with this being consistent with the increased photon absorption exposed area of the formed external agglomerate specific surface (refer to Figure 4). Therefore, based on these results, it was considered that 2 wt.% was the best photocatalyst loading for next experiments in the present study.

Effect of Initial Methanol Concentration
For methanol degradation, runs were performed by using different initial methanol concentrations of 25, 45 and 90 µmol/L with 2 wt.% loadings of bare-TiO 2 and N/Ag/TiO 2 . Figure 9 shows that bare-TiO 2 photocatalysts exhibited a maximum photocatalytic efficiency at 25 µmol/L, with a slightly lower degradation rate with increasing methanol concentrations.
constants were also determined for each experimental condition, based on at least three repeats. Data obtained show higher kinetic constants at the higher photocatalyst loadings, with this being consistent with the increased photon absorption exposed area of the formed external agglomerate specific surface (refer to Figure 4). Therefore, based on these results, it was considered that 2 wt.% was the best photocatalyst loading for next experiments in the present study.

Effect of Initial Methanol Concentration
For methanol degradation, runs were performed by using different initial methanol concentrations of 25, 45 and 90 µmol/L with 2 wt.% loadings of bare-TiO2 and N/Ag/TiO2. Figure 9 shows that bare-TiO2 photocatalysts exhibited a maximum photocatalytic efficiency at 25 µmol/L, with a slightly lower degradation rate with increasing methanol concentrations.

Quantum Yield Efficiencies
The quantum yield (QY) is a parameter that can be utilized to express the efficiency of the photocatalytic process (de Lasa et al., [19]). The QY can be calculated based on hydroxyl radical formation rates over the photocatalyst photon absorption rates. Figures  11 and 12 display the percentual quantum yields (QYs%), for 2 wt.% of bare-TiO2 and N/Ag/TiO2 coated on the mesh, as a function of irradiation reaction time for the photodegradation of methanol at 25, 45 and 90 µmol/L concentrations. An example of a QY% calculation is described in Appendix C. Figure 11 reports QYs% for the bare-TiO2 under near-UV light irradiation, showing a QY% increasing, with a maximum value after 15 min of irradiation. Then, the QYs% steadily decrease until reaching zero, at the longer irradiation times. It is relevant to observe that at 90 µmol/L, the QYs% surpass 100%, with this being consistent with results from Lugo Vega et al., [57] who used a Degussa P25 (TiO2) photocatalyst in the Photo-CREC-Air, under near-UV light, for acetone photodegradation.

Quantum Yield Efficiencies
The quantum yield (QY) is a parameter that can be utilized to express the efficiency of the photocatalytic process (de Lasa et al. [19]). The QY can be calculated based on hydroxyl radical formation rates over the photocatalyst photon absorption rates. Figures 11 and 12 display the percentual quantum yields (QYs%), for 2 wt.% of bare-TiO 2 and N/Ag/TiO 2 coated on the mesh, as a function of irradiation reaction time for the photodegradation of methanol at 25, 45 and 90 µmol/L concentrations. An example of a QY% calculation is described in Appendix C. Figure 11 reports QYs% for the bare-TiO2 under near-UV light irradiation, showing a QY% increasing, with a maximum value after 15 min of irradiation. Then, the QYs% steadily decrease until reaching zero, at the longer irradiation times. It is relevant to observe that at 90 µmol/L, the QYs% surpass 100%, with this being consistent with results from Lugo Vega et al., [57] who used a Degussa P25 (TiO2) photocatalyst in the Photo-CREC-Air, under near-UV light, for acetone photodegradation.   Figure 12a for the N/Ag/TiO2 under near-UV light one can see that the photocatalytic degradation of methanol, achieved a maximum QY close to 50%. This was twice as low as the QY% obtained when using the bare-TiO2. On the other hand, Figure 12b shows the QYs% when using a N/Ag/TiO2 photocatalyst under visible light. In this case, the maximum QY% was 35%. This is in clear contrast with the essentially zero QY% obtained when using the bare-TiO2 under visible irradiation. Furthermore, Table 6 reports a comparison of QYs% for photocatalytic methanol oxidation obtained using several photocatalyst loadings for both bare-TiO2 and N/Ag/TiO2 under visible and near-UV irradiation.  Table 6 shows for the 2 wt.% bare-TiO2, a highest QY% of 117.9% under near-UV light was obtained. This QY% is remarkably close to the theoretical maximum QY value of 133% [19]. Therefore, this result suggests that the photocatalytic methanol conversion with 2 wt.% bare-TiO2 and under near-UV light, is the recommended option to obtain the  Figure 11 reports QYs% for the bare-TiO 2 under near-UV light irradiation, showing a QY% increasing, with a maximum value after 15 min of irradiation. Then, the QYs% steadily decrease until reaching zero, at the longer irradiation times. It is relevant to observe that at 90 µmol/L, the QYs% surpass 100%, with this being consistent with results from Lugo Vega et al. [57] who used a Degussa P25 (TiO 2 ) photocatalyst in the Photo-CREC-Air, under near-UV light, for acetone photodegradation. Figure 12a,b report the QYs% for the N/Ag/TiO 2 under near-UV light and visible light irradiation, respectively. In Figure 12a for the N/Ag/TiO 2 under near-UV light one can see that the photocatalytic degradation of methanol, achieved a maximum QY close to 50%. This was twice as low as the QY% obtained when using the bare-TiO 2 .
On the other hand, Figure 12b shows the QYs% when using a N/Ag/TiO 2 photocatalyst under visible light. In this case, the maximum QY% was 35%. This is in clear contrast with the essentially zero QY% obtained when using the bare-TiO 2 under visible irradiation. Furthermore, Table 6 reports a comparison of QYs% for photocatalytic methanol oxidation obtained using several photocatalyst loadings for both bare-TiO 2 and N/Ag/TiO 2 under visible and near-UV irradiation. Table 6. Percentage quantum yields (QYs%) for the photocatalytic degradation of methanol (90 µmol/L) using either a bare-TiO 2 photocatalyst or a N/Ag/TiO 2 photocatalyst, coated on a mesh at different loadings: 0.5 wt.%, 1 wt.%, and 2 wt.%.

Photocatalysts
Maximum Quantum Yield Efficiencies (QYs%)  Table 6 shows for the 2 wt.% bare-TiO 2 , a highest QY% of 117.9% under near-UV light was obtained. This QY% is remarkably close to the theoretical maximum QY value of 133% [19]. Therefore, this result suggests that the photocatalytic methanol conversion with 2 wt.% bare-TiO 2 and under near-UV light, is the recommended option to obtain the highest possible level of utilization efficiency in a Photo-CREC-AIR-Reactor. While this is encouraging, one should mention that the bare-TiO 2 displays no activity under visible light.

Near-UV Light
On the other hand, for the 2 wt.% N/Ag/TiO 2 photocatalyst, good photocatalytic performances were consistently observed in terms of methanol conversion, for both near-UV light as well as under visible light irradiation, these conversions being 46.3% QY and a 35.8% QY, respectively.

Materials and Methods
Both the bare-TiO 2 and the N/Ag/TiO 2 photocatalysts, were prepared via the solvothermal method. The prepared photocatalysts were immobilized on a cylinder of stainless-steel woven wire mesh using the spray coating method. This method is proposed here as an appropriate technique for coating a substrate material with a cylindrical shape. To optimize the immobilized photocatalyst loadings (0.5-2 wt.%), different amounts of photocatalyst were coated on a woven stainless-steel mesh.
The conversion of methanol on the bare-TiO 2 coated mesh, using either near-UV or visible light illumination, was carried out in the Photo-CREC-Air Reactor (Lugo-Vega et al. [57]). The light intensity and distribution over the coated mesh cylinder was measured using a Stellarnet Spectrophotoradiometer (EPP3000, 200-1100 nm wavelength range, StellarNet, Inc., Carlson Circle, Tampa, FL, USA). The efficiency of the photocatalysis of methanol conversion in the reactor was established using the QYs, based on the absorbed photons and the hydroxyl radicals consumed. The various steps of the experimental methods considered are described in more detail in the upcoming section.

Preparation of Photocatalysts
The bare-TiO 2 as well as N/Ag/TiO 2 photocatalysts, were synthesized by using solvothermal method. Using this approach, a titanium (IV) butoxide (Ti(OBu) 4 , ≤97%, Fluka, Buchs, Switzerland) precursor was dissolved in 110 mL of ethanol solvent (C 2 H 5 OH, 99.8%, Merck, Darmstadt, Germany). This was followed by adding 1.26 mL of nitric acid (HNO 3 , 65%, Merck) and distilled water (3.6 mL) under vigorous mixing. The resulting homogeneous gel was then transferred to a Teflon lined autoclave and kept in an oven (Wiseven WOF-105, Daihan Scientific, Seoul, Korea), under an air atmosphere and 200 • C for 3 h. Furthermore, and to implement Ag and N doping, silver nitrate (AgNO 3 , 99%, Merck, Darmstadt, Germany) and diethylamine ((CH 3 CH 2 ) 2 NH, 99%, Merck, Darmstadt, Germany) were employed as Ag and N sources. Under these conditions, silver nitrate and diethylamine solution was added dropwise into a bare-TiO 2 solution prior to thermal treatment at 200 • C for 3 h. Regarding N and Ag in N/Ag/TiO 2 , the precursor solutions were prepared to yield a nominal 5% and 10% mol in the synthesized semiconductor, re-spectively. Once the thermal treatment was complete, the precipitate obtained was filtered, repeatedly washed with ethanol-water and dried at 80 • C overnight. The solid catalyst was finally ground in an agate mortar before annealing it at 450 • C for 3 h, in a muffle furnace (JSMF-30HT, maximum temperature 1200 • C, JSR, Gongju, Korea) with a heating rate of 10 • C/min. Further description of the reagents and methods used for photocatalysts synthesis are described in more detail in a recent publication (Sirivallop et al. [13]).

Photocatalyst Characterization Methods
The properties of the synthesized photocatalysts were characterized using XRD. With this end, an advance with Eulerian Cradle, Bruker, Madison, WI, USA unit with a Cu-Kα radiation (λ = 1.5418 Å) at 40 kV source, recording a 2θ range in the 20 • -70 • , was used. The XRD peak positions for the crystal phases were identified with the Joint Committee on Powder Diffraction Standards (JCPDS) database according to Sirivallop et al. [13]. The average crystallite size was determined using the Debye-Scherrer formula [29][30][31] below: where D is the average crystallite size (nm), K is the shape factor (0.89), λ is the wavelength of incident X-rays (1.5418 Å), and β hkl is the full width at half maximum (FWHM) of the Bragg peak. One should mention that the average particle size distributions of the prepared bare-TiO 2 and of the N/Ag/TiO 2 were measured using a Malvern Zetasizer Nano-Series Analyzer (Malvern Panalytical Ltd., Worcestershire, UK). On the other hand, the specific surface areas of the photocatalysts were determined from nitrogen adsorption-desorption isotherms at 77 K, using a surface analyzer (Quantachrome, BEL model, Boynton Beach, FL, USA). The Brunauer-Emmett-Teller (BET) method was applied to calculate the surface areas, while the pore size diameters and volumes were determined by the Barrett-Joyner-Halenda (BJH) method. The total pore volume was estimated from the adsorbed amounts at the 0.98 P/P o relative pressure.
The optical properties of the bare-TiO 2 and the N/Ag/TiO 2 photocatalysts were investigated by using an ultraviolet/visible/near-infrared (UV/Vis/NIR) spectrophotometer (Perkin Elmer, Lambda 950, Waltham, MA, USA) at the wavelength range of 200-700 nm. The band gap energy (E g ) of both photocatalysts was estimated using the Tauc-method, by plotting the (αhυ) 2 versus the photon energy (hυ) [58]. In addition, the electronic structure and electron-hole separation were analyzed using the photoluminescence (PL) spectrophotometer (AvaSpec-2048TEC-USB2-2, Avantes, Apeldoorn, The Netherlands) under the excitation of a 20 microwatt light-emitting diode (LED) lamp. The chemical composition and state of the Ag and N in the bare-TiO 2 crystal lattice were analyzed by X-ray photoelectron spectroscopy (XPS) using a Thermoscientific ESCALAB 250Xi system with a Mg Kα source (Thermo Fisher Scientific, Waltham, MA, USA). All the binding energies were calibrated using the C 1s peak at 284.6 eV.
Furthermore, and to establish the relative abundance of the acid sites on the photocatalyst surface, ammonia (NH 3 ) TPD was performed by using a Micromeritics Autochem II 2920 instrument (Norcross, GA, USA). In the TPD procedure, the prepared photocatalysts were pretreated with a flow of helium (He) at 600 • C for 20 min and then cooled down to 100 • C. After this, a stream of gas containing 5% NH 3 balanced with He, was circulated through two beds containing 178 mg and 183 mg of synthesized bare-TiO 2 and N/Ag/TiO 2 , respectively, at a rate of~50 cm 3 /min and heated at 100 • C for 1 h. Then, the photocatalyst samples were heated using a 20 • C/min ramp, from ambient to 600 • C, under helium flow. NH 3 was then progressively released from the sample, once the sample temperature provided the required ammonia desorption energy. TPD was then employed to quantify the desorbed NH 3 from the photocatalyst samples. As a result, the total acidity of the sample was determined by integrating the eluted ammonia peak, which represented the volumetric change of NH 3 in cm 3 /min (STP).

Spray Coating for Photocatalyst Immobilization
Good mesh coatings should provide a uniform and homogenous photocatalyst layer. The resulting coating should provide a large of surface area with little particle agglomeration. In this respect, spray coating techniques show great potential with neither binder nor polymer required due to the interparticular-forces between bare-TiO 2 photocatalysts and stainless-steel woven mesh [59].
A 304 stainless-steel cylindrical woven wire mesh (Ferrier Wire Goods Co., Toronto, ON, Canada) with a 1220 cm 2 total area, a 0.01 mm wire diameter, a 40 × 40 mesh count and 36% open area, was used as the substrate material in this research. The immobilization of the photocatalyst on the stainless-steel woven mesh cylinder was obtained by using the spray coating technique which was adapted from Lugo-Vega et al. [59]. These authors reported that spray coating provides an appropriate technique for TiO 2 photocatalyst immobilization on complex substrates such as metallic meshes, without blocking the mesh openings and without affecting the pressure drop significantly.
The apparatus described in Figure 13 was used by adopting the following photocatalyst immobilization steps: i.
A cylindrical shaped mesh was cleaned with acetone, alcohol and deionized water to remove all dirt, oils or grease, before letting it dry. ii.
A cleaned cylindrical shaped stainless-steel woven mesh was set on a rotating base with a constant velocity of 12 rpm. A 150 Badger nozzle gun (Badger Air-Brush Co., Franklin Park, IL, USA) was held on a stand, which was fixed at a distance of 30 cm from the cylinder mesh surface. iii.
The bare-TiO 2 or N/Ag/TiO 2 particle suspension with different concentrations (5, 10 and 20 wt.%) were prepared using distilled water (50 mL), by sonicating the particle slurries for 30 min. Furthermore, and to avoid the particle settling during spray coating, the particle suspension was stirred continuously using a magnetic stirrer. iv.
A 1.31 mL suspension volume was injected into a paint cup and then sprayed onto the mesh surface with an adequate and constant air pressure of 20 psia. This required coating was typically achieved after three-cylinder rotations, with the spray gun providing a homogeneous coating to all areas of the metallic mesh ( Figure 14). To cover the entire height of the cylindrical mesh, the gun level was adjusted for every coating step, starting from the top and moving down every 5 cm. The bare-TiO2 or N/Ag/TiO2 particle suspension with different concentrations (5, 10 and 20 wt.%) were prepared using distilled water (50 mL), by sonicating the particle slurries for 30 min. Furthermore, and to avoid the particle settling during spray coating, the particle suspension was stirred continuously using a magnetic stirrer. iv.
A 1.31 mL suspension volume was injected into a paint cup and then sprayed onto the mesh surface with an adequate and constant air pressure of 20 psia. This required coating was typically achieved after three-cylinder rotations, with the spray gun providing a homogeneous coating to all areas of the metallic mesh ( Figure 14). To cover the entire height of the cylindrical mesh, the gun level was adjusted for every coating step, starting from the top and moving down every 5 cm.
The mass of the photocatalyst coated on the cylindrical mesh was determined by the weight difference before and after coating. It was found that 1 g of immobilized photocatalyst could be coated on a 220 ± 0.2 g of stainless-steel woven mesh, using 2.5 g of photocatalyst dispersed in 50 mL of water. Using the proposed impregnation method, the photocatalyst coated with immobilized photocatalyst on the wire mesh as shown in Figure 14 was obtained. This was achieved with a spray coating efficiency of about 40 wt.% Figure 13. Schematic diagram of the immobilization of the photocatalyst on a stainless steel woven wire mesh cylinder via an air assisted spray coating technique adapted from Lugo-Vega et al. [59]. Furthermore, and to investigate the optimal amount of photocatalyst immobilized on the mesh, three different amounts of bare-TiO2 and N/Ag/TiO2 suspensions were prepared: 0.5 wt.%, 1 wt.% and 2 wt.% Moreover, the strength of the photocatalyst particle attachment on the stainless-steel woven mesh was evaluated by exposing the coated mesh to the airflow system in the Photo-CREC-Air Reactor for 48 h. One should note that the weight of the immobilized mesh before and after testing was essentially unchanged, with a 0.02 ± 0.01% weight loss only.

Photocatalytic Conversion of Methanol in the Photo-CREC-Air Reactor (PCAR)
The Photo-CREC-Air Reactor (55 L total volume) operates at isothermal conditions 39 ± 0.5 °C. It was designed for the photocatalytic degradation of several VOCs pollutants, using an irradiated cylinder mesh with an immobilized photocatalyst. The PCAR was employed for the conversion of methanol, in this present work. Figure 15 describes a simplified scheme of the overall view of a Photo-CREC-Air Reactor. The Photo-CREC-Air Reactor consists of three major sections: (1) an air transfer section, using a GASP gas blower to drive the air to the Venturi and to the reaction section, (2) a water-cooling section which controls the temperature before recirculating the air into the reaction section, and (3) a reaction section with a coated mesh inside a quartz glass tube, surrounded by eight light lamps, ensuring adequate irradiation to the coated mesh. The cylindrical stainless-steel woven mesh is supported by a bullet nose bottom, which promotes the appropriate airflow recirculation through the coated mesh ( Figure  15, inset).
The experiments of methanol conversion in a Photo-CREC-Air Reactor were carried out by using either a bare-TiO2-coated mesh or N/Ag/TiO2-coated mesh, under the irradiation of 8 near-UV lamps (Philips, Amsterdam, the Netherlands, 15 W, 325-380 nm wavelength) or 8 visible light lamps (Eiko Global, Shawnee, KS, USA, 15 W, 360-800 nm wavelength). Before the light was turned on, the experiment was run under dark conditions for 30 min. This was done in order to reach the adsorption equilibrium between the organic pollutants and the photocatalyst. Regarding the runs developed, experiments involved varying the quantity of photocatalyst loading (0.5, 1 and 2 wt.%) and the methanol concentration (25,45, and 90 µmol/L). Every experimental condition was repeated at least three times, to secure adequate data collection. Before every experimental run, air in the photoreactor reactor loop was allowed to flow, with the "on-off" valve opened for an hour. This permitted the evacuation of any chemical species that could have remained in the Photo-CREC-Air Reactor from a previous run. The mass of the photocatalyst coated on the cylindrical mesh was determined by the weight difference before and after coating. It was found that 1 g of immobilized photocatalyst could be coated on a 220 ± 0.2 g of stainless-steel woven mesh, using 2.5 g of photocatalyst dispersed in 50 mL of water.
Using the proposed impregnation method, the photocatalyst coated with immobilized photocatalyst on the wire mesh as shown in Figure 14 was obtained. This was achieved with a spray coating efficiency of about 40 wt.%.
Furthermore, and to investigate the optimal amount of photocatalyst immobilized on the mesh, three different amounts of bare-TiO 2 and N/Ag/TiO 2 suspensions were prepared: 0.5 wt.%, 1 wt.% and 2 wt.% Moreover, the strength of the photocatalyst particle attachment on the stainless-steel woven mesh was evaluated by exposing the coated mesh to the airflow system in the Photo-CREC-Air Reactor for 48 h. One should note that the weight of the immobilized mesh before and after testing was essentially unchanged, with a 0.02 ± 0.01% weight loss only.

Photocatalytic Conversion of Methanol in the Photo-CREC-Air Reactor (PCAR)
The Photo-CREC-Air Reactor (55 L total volume) operates at isothermal conditions 39 ± 0.5 • C. It was designed for the photocatalytic degradation of several VOCs pollutants, using an irradiated cylinder mesh with an immobilized photocatalyst. The PCAR was employed for the conversion of methanol, in this present work. Figure 15 describes a simplified scheme of the overall view of a Photo-CREC-Air Reactor. The Photo-CREC-Air Reactor consists of three major sections: (1) an air transfer section, using a GASP gas blower to drive the air to the Venturi and to the reaction section, (2) a water-cooling section which controls the temperature before recirculating the air into the reaction section, and (3) a reaction section with a coated mesh inside a quartz glass tube, surrounded by eight light lamps, ensuring adequate irradiation to the coated mesh. The cylindrical stainless-steel woven mesh is supported by a bullet nose bottom, which promotes the appropriate airflow recirculation through the coated mesh (Figure 15, inset).
The experiments of methanol conversion in a Photo-CREC-Air Reactor were carried out by using either a bare-TiO 2 -coated mesh or N/Ag/TiO 2 -coated mesh, under the irradiation of 8 near-UV lamps (Philips, Amsterdam, the Netherlands, 15 W, 325-380 nm wavelength) or 8 visible light lamps (Eiko Global, Shawnee, KS, USA, 15 W, 360-800 nm wavelength). Before the light was turned on, the experiment was run under dark conditions for 30 min. This was done in order to reach the adsorption equilibrium between the organic pollutants and the photocatalyst. Regarding the runs developed, experiments involved varying the quantity of photocatalyst loading (0.5, 1 and 2 wt.%) and the methanol concentration (25,45, and 90 µmol/L). Every experimental condition was repeated at least three times, to secure adequate data collection. Before every experimental run, air in the photoreactor reactor loop was allowed to flow, with the "on-off" valve opened for an hour. This permitted the evacuation of any chemical species that could have remained in the Photo-CREC-Air Reactor from a previous run. The concentrations of methanol and of photocatalytic intermediates at various irradiation times, were quantified using an automatic sampling valve connected to a gas chromatographic (GC) unit. This GC was equipped with a flame ionization detector (FID). The GC-FID methods employed are described in Supplementary Materials A and B. Figure 15. Schematics of a Photo-CREC-Air Reactor system with gas chromatography equipment. This figure also describes the air circulation (Airflow) through the stainless-steel woven coated mesh (inset).

Radiation Measurements and Macroscopic Irradiation Energy Balances
Irradiation measurements in the Photo-CREC-AIR Reactor unit are of prime importance to establish macroscopic energy balances [19]; incident photons (Pi) are absorbed, backscattered, and transmitted by the photocatalyst impregnated mesh, as described in Figure 16. To establish photon absorption in the photocatalyst, measurements of incident light, transmitted light through the mesh, and backscattered light were carried out at several axial and angular positions. This allowed us to establish macroscopic radiation balances as follows: The concentrations of methanol and of photocatalytic intermediates at various irradiation times, were quantified using an automatic sampling valve connected to a gas chromatographic (GC) unit. This GC was equipped with a flame ionization detector (FID). The GC-FID methods employed are described in Supplementary Materials A and B.

Radiation Measurements and Macroscopic Irradiation Energy Balances
Irradiation measurements in the Photo-CREC-AIR Reactor unit are of prime importance to establish macroscopic energy balances [19]; incident photons (P i ) are absorbed, backscattered, and transmitted by the photocatalyst impregnated mesh, as described in Figure 16. The concentrations of methanol and of photocatalytic intermediates at various irradiation times, were quantified using an automatic sampling valve connected to a gas chromatographic (GC) unit. This GC was equipped with a flame ionization detector (FID). The GC-FID methods employed are described in Supplementary Materials A and B.

Radiation Measurements and Macroscopic Irradiation Energy Balances
Irradiation measurements in the Photo-CREC-AIR Reactor unit are of prime importance to establish macroscopic energy balances [19]; incident photons (Pi) are absorbed, backscattered, and transmitted by the photocatalyst impregnated mesh, as described in Figure 16. To establish photon absorption in the photocatalyst, measurements of incident light, transmitted light through the mesh, and backscattered light were carried out at several axial and angular positions. This allowed us to establish macroscopic radiation balances as follows: To establish photon absorption in the photocatalyst, measurements of incident light, transmitted light through the mesh, and backscattered light were carried out at several axial and angular positions. This allowed us to establish macroscopic radiation balances as follows: P i = P a + P t + P bs (15) P a = P i − P t − P bs (16) where, P i is the rate of incident light, P a is the rate of absorbed photons by the photocatalyst, P t is the rate of transmitted photons by the photocatalysts and P bs is the rate of backscattered photons by the photocatalyst. One should note that the photon flux for P i , P t and P bs in photons s −1 can be calculated using following equation: The total photon energy (Q) in the reactor can be calculated by integrating the spectral irradiance overall photon wavelengths and multiplying this by the irradiated area of a cylindrical mesh as shown in Equation (18). On this basis, the average photon energy (E av ) in J/photon can be obtained by using Equation (19) [60,61].
According to Equation (17), it can be rewritten with the use of Equations (18) (20) or, where Q or q(θ, z, λ) represents the energy from the lamp in J s −1 units, measured at different angular (θ), radial (r) and axial (z) positions; where P is the photon flux (photon s −1 ); where E av stands for the average photon energy (J/photon); where λ is the photon wavelength (nm); where h is the Planck's constant (6.34 × 10 −34 J s/photon); and where c the speed of light (3.0 × 10 8 m s −1 ). To calculate the various irradiation terms as shown in Figure 16, and to obtain a value for P a , a Stellarnet Spectrometer (EPP3000, 200-1100 nm wavelength range, Carlson Circle Tampa, FL, USA) connected with an optical probe, was employed. The sensing end of this spectroradiometer was adapted, so that it could be inserted into the reaction section of the reactor from the top of the quartz glass tube. As a result, we were able to develop radiation measurements, at several axial and angular positions in the Photo-CREC-Air unit, as required by Equation (15). The spectral intensity of near-UV (320-400 nm wavelength) and visible light (380-800 nm wavelength) lamps measured by a Stellarnet Spectrometer is shown in Appendix A. Additional information regarding radiation measurements and other auxiliary equipment are reported in more detail by Lugo-Vega [57].

Quantum Yield Efficiencies
The quantum yield (QY) is a key parameter used to establish the performance of a photocatalytic reactor (de Lasa et al. [19]). The QY can be defined as the ratio of the moles of OH • radicals involved in the photocatalytic reaction over the number of moles of photons absorbed by photocatalyst [61]. Thus, the QY can be calculated as reported in Equation (22) [60,61]: Quantum yield (QY) = rate of OH • consumed rate of photon absorbed (22) The rate of OH • consumption can be calculated using the stoichiometry of pollutant degradation as follows: where, r i,j and r OH • ,j stand for the C n H m O o and OH • consumption rates, respectively; and where ν i,j and ν OH • ,j represent the stoichiometric coefficients for C n H m O o and OH • at step j, respectively. Thus, and to be able to calculate the total rate of OH • consumed, one should consider the summation of all OH • depleted, at every photocatalytic step as follows: Hence, the QY calculation for overall reaction should be as shown in Equation (27).

Conclusions
(a) It was shown that an air-assisted spray coating technique is effective to coat a N/Ag/TiO 2 photocatalyst on a cylindrical stainless-steel woven wire mesh. (b) It was demonstrated that a coated N/Ag/TiO 2 photocatalyst in a stainless-steel woven wire mesh in a Photo-CREC-Air unit is effective in decomposing methanol under both near-UV and visible light. (c) It was proven that a stainless-steel woven mesh immobilized N/Ag/TiO 2 at 2 wt.% loading in the Photo-CREC-Air Reactor, provides a best photocatalytic activity with 60% methanol conversion and a best QY% of 35 Figure S1: GC parameters of the column separation method; Figure Figure A1 represents the spectrum for the near-UV light and the visible light from 300 to 800 nm range. . Figure A1. Spectral intensity of near-UV and visible light lamps measured by a Stellarnet Spectrometer (EPP3000, 200-1100 nm wavelength range).

Appendix B. Relative Humidity Analysis in the Photo-CREC Air Reactor (PCAR)
A calibration was performed in the PCAR to quantify the relative humidity (RH) of air streams. The RH is an important parameter to be considered to determine whether the water vapor in the PCAR has an effect on the photocatalytic activity. The RH data were taken with a hygrometer (Mengshen digital humidity meter) at different known water concentrations. The hygrometer operates from 0 to 100% RH and −20 to 80 • C range, respectively. Furthermore, its humidity accuracy is ±3% RH and the resolution falls into 0.01% RH or 0.01 • C. Figure A2 shows a pinkish-shaded band which represents the operational relative humidity range, 35% to 46%. This range agrees with the reported experimental data of 25, 45 and 90 mmol represented with the green, blue, and yellow color cross marks. Thus, these results are in line with claims from others [62][63][64] showing that keeping air relative humidity in the 20-50% range results in a lack of influence of humidity on photocatalytic activity. Therefore, under the proposed conditions, one can process a VOC air contaminated stream with a 30-50% RH. This is the recommended RH for indoor environments for air quality [65,66].

Appendix B. Relative Humidity Analysis in the Photo-CREC Air Reactor (PCAR)
A calibration was performed in the PCAR to quantify the relative humidity (RH) of air streams. The RH is an important parameter to be considered to determine whether the water vapor in the PCAR has an effect on the photocatalytic activity. The RH data were taken with a hygrometer (Mengshen digital humidity meter) at different known water concentrations. The hygrometer operates from 0 to 100% RH and −20 to 80 °C range, respectively. Furthermore, its humidity accuracy is ±3% RH and the resolution falls into 0.01% RH or 0.01 °C. Figure A2 shows a pinkish-shaded band which represents the operational relative humidity range, 35% to 46%. This range agrees with the reported experimental data of 25, 45 and 90 mmol represented with the green, blue, and yellow color cross marks. Thus, these results are in line with claims from others [62][63][64] showing that keeping air relative humidity in the 20-50% range results in a lack of influence of humidity on photocatalytic activity. Therefore, under the proposed conditions, one can process a VOC air contaminated stream with a 30-50% RH. This is the recommended RH for indoor environments for air quality [65,66].

Appendix C. Percentual Quantum Yield (QY%) Calculations
This provide an example %QY calculation for a 2 wt.% N/Ag/TiO2 photocatalyst coated on a mesh to degrade 90 µmol/L of methanol under visible light irradiation for 120 min.

Appendix C. Percentual Quantum Yield (QY%) Calculations
This provide an example %QY calculation for a 2 wt.% N/Ag/TiO 2 photocatalyst coated on a mesh to degrade 90 µmol/L of methanol under visible light irradiation for 120 min.  Figure A3a reports the XPS for both N/Ag/TiO 2 and bare-TiO 2 photocatalysts, showing the Ag 3d and N 1s peaks for the N/Ag/TiO 2 photocatalyst only, with these peaks being absent for the bare-TiO 2 . Thus, the Ag 3d as well as N 1s signals confirm the coexistence of Ag and N dopants in the photocatalyst. 100 % = 35.08% (A4) Figure A3a reports the XPS for both N/Ag/TiO2 and bare-TiO2 photocatalysts, showing the Ag 3d and N 1s peaks for the N/Ag/TiO2 photocatalyst only, with these peaks being absent for the bare-TiO2. Thus, the Ag 3d as well as N 1s signals confirm the coexistence of Ag and N dopants in the photocatalyst. Regarding Ag 3d peak intensity and peak separation as reported in Figure A3b Thus, on this basis one can consider: (a) N incorporated in the TiO2 lattice, (b) since the 115 pm Ag + ionic radius is larger than the 60.5 pm Ti 4+ it can be argued that Ag + is not incorporated into the bare-TiO2 lattice but deposited on the bare-TiO2 surface [70].  Regarding Ag 3d peak intensity and peak separation as reported in Figure A3b Thus, on this basis one can consider: (a) N incorporated in the TiO 2 lattice, (b) since the 115 pm Ag + ionic radius is larger than the 60.5 pm Ti 4+ it can be argued that Ag + is not incorporated into the bare-TiO 2 lattice but deposited on the bare-TiO 2 surface [70].