Gaseous cyclohexanone catalytic oxidation by a self-assembled Pt/γ-Al2O3 catalyst: process optimization, mechanistic study, and kinetic analysis

γ-Al2O3 nanocatalysts with a Pt loading of 0.6–1.0% were prepared successfully via a self-assembly method to be used in the catalytic oxidation of cyclohexanone in a fixed-bed reactor. The nanocatalysts were characterized by the Brunauer–Emmett–Teller method, X-ray diffraction, transmission electron microscopy, Fourier-transform infrared spectroscopy, and temperature programmed reduction-H2 to correlate their activity with their physiochemical properties. Based on these analyses, the catalytic oxidation efficiency for cyclohexanone and the optimal catalytic temperature of 1.0% Pt/γ-Al2O3 were the best among all the nanocatalysts. A novel response surface methodology (RSM) method was employed to evaluate the interactions of the gaseous cyclohexanone concentration (500–4000 mg m−3), the gas hourly space velocity (GHSV, 5000–20 000 h−1), and relative humidity (RH 10–70%) on the catalytic oxidation under normal atmospheric pressure and a catalytic temperature of 235 °C. When the initial catalyst concentration, GSHV, and RH were 2000 mg m−3, 12 000 h−1, and 50%, respectively, the efficiency was 86.5%, nearly equal to that (89.6%) predicted by the RSM model. Intermediate generation, CO2 production, and variations in the cyclohexanone oxidation route were evaluated under the optimal process parameters. During catalytic oxidation, nearly all the cyclohexanone was converted to CO2 and H2O, and the mineralization rate was 80% under a RH of 50%. A kinetic model was proposed to describe the interaction effects between the partial pressure and catalytic temperature on the conversion of cyclohexanone. It was found that the predicted values by the model fit well with the experimental values, with an R2 of 0.99.


Introduction
Atmospheric pollution has become a serious problem in recent years because of the rapid development of the chemical industry and increased human activities. 1 As some of the main air pollutants, volatile organic compounds (VOCs) are directly released without any treatments, which not only increases the degree of atmospheric pollution, but also leads to harmful effects on human health. 2 Recent studies showed that the increase of ozone in the troposphere is related directly to the emission of VOCs. 3,4 Therefore, efficient and economic methods for reducing pollutants like VOCs are required.
Among the various current technologies for VOC abatement, catalytic oxidation has been considered to be one of the most effective and promising technologies because of its low operation temperature, high purication efficiency, recoverable heat, and lack of secondary pollution. 5,6 The performances of different methods for VOC removal are affected by several factors, such as the types of VOCs, the types of catalysts, the process parameters, and purication requirements. 7,8 O'Malley and Hodentt 9 showed that the reactivity of VOCs, in terms of total oxidation, with different functional groups, such as alcohols, aromatics, ketones, carboxylic acids, and alkanes, varies. Three types of catalysts are used widely for VOC oxidation, namely precious metals, transition metal oxides, and zeolites, and most studies have focused on the relationship between their structural characteristics and performances. [10][11][12][13] Process parameters, such as target concentration, space velocity, and temperature, are mostly considered for the evaluation of the prepared catalysts. According to the previous studies, more attention should be paid to aromatics, chlorinated VOCs, and alkanes because aromatics (like benzene and toluene) are emitted mostly by industry, and chlorinated VOCs are toxic to catalysts (mainly because of the formation of highly chlorinated by-products), which affects its usage time, while alkanes are not oxidized efficiently by other methods (such as bio-oxidation and photo-oxidation). 14 As an important industrial material, ketones are also used widely and emitted not only from the centralized emission (usually chimney) but also decentralized emission. 15 Cyclohexanone is an important chemical material in the manufacture of nylon, caprolactam, adipic acid, and resin. Because of its low boiling point, cyclohexanone is highly volatile, and, thus, it is a typical VOC, which constitutes a serious threat to human health and the environment. Long-term exposure to low concentrations of cyclohexanone may result in serious diseases, e.g., neurasthenia and leukemia, while inhaling high levels of cyclohexanone in a short time causes headaches and unconsciousness, and it can anesthetize the central nervous system. Cyclohexanone and other VOCs transform into the precursor of ozone in the atmosphere, and they react with other precursors of ozone (like NO x ) under light to form the most serious form of air pollution. 16 Therefore, there is a need to control the production of cyclohexanone.
The essence of VOC oxidation is the breaking of chemical bonds. Once the rst bond is broken, sequential reactions to form CO 2 and H 2 O are accomplished more easily. 17 Among the factors affecting VOC destruction (promoters, surface areas or sizes of the catalysts, and catalyst loading), the active component is the most crucial factor. The noble metals Pt and Pd in g-Al 2 O 3 catalysts have been used widely and efficiently for the oxidation of VOCs. 18 Pd exhibits higher activity toward shortchain hydrocarbons, while Pt is more active for the oxidation of long-chain hydrocarbons and aromatics. Pt/g-Al 2 O 3 is widely known as one of the most effective commercial catalyst for the oxidation of hydrocarbon molecules such as benzene. 18,19 As a result, Pt/g-Al 2 O 3 is usually added to a non-thermal plasma reactor for VOC removal. It has been shown that the incorporation of this catalyst might improve energy efficiency, maximize product yield, and minimize byproducts. 20,21 Compared with other VOCs, there are few studies of the purication of cyclohexanone and its oxidation using different catalysts. Although Pt/g-Al 2 O 3 is the most widely applied catalyst, 22 its use for cyclohexanone treatment has not been reported, and the oxidation mechanism of cyclohexanone has not been revealed. In addition, most previous studies only focused on the catalytic oxidation effect caused by a single factor, without investigating the interaction effects of different factors. As is well known, several process parameters collectively determine the VOC removal performance, and consideration of their combined effect is much more important. 23 Such knowledge (like the optimal operational parameters) is useful for industrial applications. Based on these reasons, studies of the catalytic oxidation of cyclohexanone by Pt/g-Al 2 O 3 are needed not only to hasten its possible industrial application, but also to determine its oxidation mechanism.
In the present study, we used the Brunauer-Emmett-Teller method, transmission electron microscopy (TEM), X-ray diffraction (XRD), Fourier-transform infrared spectroscopy (FTIR), and temperature programmed reduction-H 2 (H 2 -TPR) to evaluate the performance of a new, self-assembled Pt/g-Al 2 O 3 catalyst containing 1.0 wt% Pt in the catalytic oxidation of cyclohexanone and to conduct a structural characterization of the catalyst. The activity of the prepared catalyst was tested under several reaction conditions, and the optimal conditions (including the concentration of cyclohexanone, the relative humidity [RH], and the space velocity) were determined by the response surface methodology method, thus providing a quantitative understanding of the interaction effects and determining the relationship between the variables and the cyclohexanone removal efficiency. The product distribution and formation pathway of by-products are discussed to explore the oxidation mechanism of cyclohexanone. Additionally, a kinetic analysis of the catalytic process was also studied, and the obtained kinetic model was in good agreement with the experimental results. The fundamental information derived from this study is important for the application of Pt/g-Al 2 O 3 and other similar catalysts in cyclohexanone and other VOC abatement.

Catalyst preparation
The Pt/g-Al 2 O 3 catalyst was prepared according to a previously reported procedure, with a few modications. 24,25 K 2 PtCl 4 (1.4 g) was dissolved in 12 mL of distilled water, followed by the addition of an ethanol solution containing 2.36 g of bis-dba (dba ¼ dibenzylideneacetone) and 2.8 g of sodium acetate at 50 C. Then, the mixed solution was reuxed for 1 h at 90 C, and nally it changed from an initial pale-yellow liquid into a dark purple precipitation. Then, the precipitate was ltered aer 12 h, washed three times with 20 mL of n-pentane, and dried overnight under vacuum; the wash and dry cycle was conducted for twice. Then, Pt 2 (dba) 3 was prepared for further use.
A certain amount of Pt 2 (dba) 3 was added to a propylene carbonate solution, placed in a stainless-steel cylinder, and mixed evenly. Then, hydrogen was used to replace the air for the balance of the partial pressure (3 MPa). The solution was stirred at room temperature for nearly 2 h until a brown colloid was produced, and then g-Al 2 O 3 was added with stirring for 24 h. The solid catalyst was separated by ltration and dried at 80 C. Only trace levels of Pt were observed in the clear ltrate, indicating a complete adsorption of the Pt on the carrier. Different mass fraction Pt-nano particles (0.6-1.0%) of g-Al 2 O 3 were prepared by the assembled method. The packing density of the prepared catalyst was 0.826 kg cm À3 and the particle size was 0.5-3.0 mm. For comparison, a blank g-Al 2 O 3 catalyst with no Pt loading was prepared.

Catalyst characterization
TEM images were acquired using a Tecnai G2 F30 S-Twin (Philips-FEI, Amsterdam, the Netherlands) instrument at an acceleration voltage of 200 kV. The structures of the catalysts were assessed using an XRD analyzer (PANalytical, Almelo, the Netherlands). The conditions of analysis were as follows: Cu-Ka radiation (l ¼ 1.54178Å); scanning rate, 0.03 s À1 ; and scanning range (2q), 20-80 C.
The BET surface area of the catalyst was measured by N 2 adsorption at a liquid-nitrogen temperature of 196 C, using a surface area analyzer (ASAP 2010; Micromeritics, Norcross, GA, USA). To assess surface functional groups, FTIR (Nicolet 6700; Thermo Scientic, Waltham, MA, USA) was conducted at wave numbers of 400-4000 cm À1 . TPR-H 2 measurements were conducted on a Micromeritics Pulse ChemiSorb 2705 to address the reducibility of nanocatalysts. Approximately 50 mg of the sample was loaded into a reactor and pretreated at 200 C in an Ar stream for 1 h to remove the adsorbed carbonates and hydrates. Aer cooling to 50 C, a ow of 10% H 2 -90% Ar was passed through the samples, and the temperature was increased at a rate of 10 C min À1 up to 1000 C, while a thermal conductivity detector (TCD) was used.

Experimental setup
The measurement of the catalytic activity of the oxidation of cyclohexanone was performed at atmospheric pressure in a conventional uidized bed reactor reaction system, and the schematic diagram is shown in Fig. S1. † Air was supplied by an air-compressor and divided into three streams, all of which were controlled by a mass ow controller. One was saturated with cyclohexanone by injecting it into a bottle of cyclohexanone liquid, followed by mixing with a second air stream to dilute the gaseous cyclohexanone to obtain a certain concentration. The third one was injected into distill water to produce a certain humidity of gas. Finally, all these streams went into the mixed bottle, and the reactant waste gas was obtained.

RSM design
RSM (Design Expert Version 8.0) was adopted in this study, and central composite design (CCD) is one of the most popular methods for the experimental design. Three factors were considered with two levels. The a (a ¼ AE1.2) distance was designed according to the need of the experiments, and six central points were generated by the automatic system, as shown in Table 1.
Aer analyzing the responses according to the designed experiments, a mathematical model with interactions was obtained by the following equation: where y is the expressed response; X represents the independent variables; b 0 indicates the intercept constant; b i shows the coefficients of linear terms; b ii represents the coefficients of quadratic terms; b ij shows the coefficients of interaction terms; x indicates the experimental error; and k represents the number of independent variables.

Analytical methods
Inlet gas and outlet gas were analyzed by a gas chromatograph equipped with a ame ionization detector (GC-FID, Agilent GC 7890N; Santa Clara, CA, USA). The analytical column was a capillary column (Agilent 19091N-213 HP-INNOWax polyethylene glycol 32 m Â 320 mm Â 0.50 mm) with a temperature of 180 C, while the detector temperature was 200 C. The sample volume was 1000 mL, and each experiment was repeated three times under the same conditions. CO 2 accumulation was tested with an HP-Plot-Q column (30 m Â 0.32 mm Â 20 mm) and a TCD. Helium at a ow rate of 5 mL min À1 was used as the carrier gas. The column and detector temperatures were 313 K and 473 K, respectively.
The off-gas (containing various gaseous products) was captured using an adsorption tube at a set of temperatures for 1 h. Then, the absorbed compounds were released into a thermal desorption instrument, which were injected into a GC-mass spectrometry (GC-MS) system (Agilent 7890 A GC equipped with an Agilent 5975C Mass Selective Detector) with an HP-INNOWax capillary column (60 m Â 0.32 mm Â 0.5 mm). The temperature was maintained at 36 C for 2 min, and then it was increased to 250 C at a rate of 10 C min À1 , at which point it was maintained for 6 min.
For other small organic intermediates, the catalysts were analyzed by FTIR (Nicolet 6700, Thermo) in the wave number range of 400-4000 cm À1 . The differences in the peaks between the fresh and used catalyst might be some intermediates that are generated by the catalytic process.

Catalyst characterization
g-Al 2 O 3 catalysts with three different Pt contents (0.6%, 0.8%, and 1.0%, wt%) were prepared, and their structural characteristics were analyzed by BET, TEM, XRD, FTIR, and H 2 -TPR. The optimal catalyst was determined by both the structure and conversion of cyclohexanone.
3.1.1 Specic surface area and porous volume by BET measurements. The BET surface area and the distribution of the pore volume are shown in Table 2. It was observed that the addition of Pt had little effect on the surface area of g-Al 2 O 3 . For 0.6% Pt/g-Al 2 O 3 , the surface area and the pore volume were 179 m 2 g À1 and 0.94 cm 3 g À1 , respectively, and adding Pt to 0.8%, and 1.0% wt% decreased both the surface area and pore volume to 168 and 150 m 2 g À1 and 0.88 and 0.83 cm 3 g À1 , respectively. Such results suggested that increasing the Pt content leads to covering the surface of the aluminum oxide, which decreased the overall surface area. Adsorption is one of the important steps of the catalytic reaction, and the surface area of the catalyst is a VOC-adsorption site. 14 In addition, some mesopores of the g-Al 2 O 3 support might be blocked by Pt species during the preparation. However, Table 2 shows that the total pore volume did not vary much, which indicated that the high dispersion of the Pt nanoparticles did not block the pores of g-Al 2 O 3 . The larger surface area and pore volume could be a result of suitable preparation, similar to the phenomenon reported by Abbasi et al., 17 who showed that a high surface area could be a result of nanometric particles and a suitable calcination temperature. It is noted that the percentage of mesoporous (2-50 nm) particles increased slightly with the loading amount of Pt, which suggested that the prepared catalyst would have better activity. 26 Such irregular pores would create numerous active sites, and this special structure would facilitate the adsorption and diffusion of organic molecules or the produced compounds (CO 2 and H 2 O), thus avoiding the limitations of interphase mass transfer and promoting their catalytic activities.
3.1.2 TEM. The morphology and microstructure of the synthesized catalysts were investigated by TEM. Fig. 1 shows the TEM images of g-Al 2 O 3 and Pt (0.6-1.0%)/g-Al 2 O 3 . The results showed that the active phase (Pt) was well dispersed with a particle size of 2-10 nm. Pt nanoparticles (black dots) were distributed uniformly aer being loaded onto the g-Al 2 O 3 support, and the average diameters of the Pt changed little, without obvious aggregation, indicating that the preparation had no effect on the size of the Pt nanoparticles. Nobel metals promote the migration/exchange of oxygen species, and their presence provides catalysts with many more reactive sites. [27][28][29] With increasing amounts of active Pt, the nanoparticles on the surface increased gradually and the pore structure decreased gradually, which is consistent with the BET surface area and pore size distribution of the corresponding pre-and post-Pt loaded g-Al 2 O 3 .
3.1.3 XRD and FTIR analysis. The XRD patterns of the selfassembled Pt/g-Al 2 O 3 catalyst with different Pt mass fractions are shown in Fig. 2a. The diffraction peak at 2q ¼ 66.64 (440), 45.92 (400), and 37.40 (331) corresponded to the planes of g-Al 2 O 3 . 30 However, there were no Pt peaks in the XRD spectra at 2q near 40.0 (111), 46.5 (200), and 67.4 (220), unless the Pt content increased to 1.0%. These results indicated that the dispersion of Pt on the g-Al 2 O 3 support was very good, and no large crystallites formed. 31 With the increase in the amount of loaded Pt, the intensity of the peak at 2q ¼ 14.5 increased. This suggested that the interactions between Pt and g-Al 2 O 3 were strengthened, which would lead to the production of more free radicals for VOC oxidation. 32,33 Fig. 2b describes the FTIR spectra of the Pt-1.0%/g-Al 2 O 3 catalysts and g-Al 2 O 3 . Stretching vibrations for structural -OH and adsorbed H 2 O for all the samples were observed at wave numbers of approximately 3430, 1640, and 1410 cm À1 , and the peak intensity of the Pt-1.0%/g-Al 2 O 3 catalyst was much stronger than that of unloaded g-Al 2 O 3 . This difference suggested that more hydrogen bonds formed on the catalyst, which would lead to the production of more hydroxyl radicals, thereby beneting the catalytic oxidation of VOCs. 30 A characteristic vibrational band next to 588 cm À1 for Al-O-Al has been reported, and its intensity was much stronger aer Pt loading. A new vibration telescopic peak at 1474 cm À1 appeared for the prepared Pt-1.0%/g-Al 2 O 3 catalyst. This peak could be a Pt-Al-O bond that was formed by the strong interaction between Pt and g-Al 2 O 3 during the preparation. Such bond formation could enhance the catalytic activity. 24 3.1.4 TPR-H 2 . To investigate the reduction behavior of the catalysts, H 2 -TPR studies were performed for g-Al 2 O 3 and Pt-(0.6-1.0%)/g-Al 2 O 3 catalysts as shown in Fig. 3. There was no obvious hydrogen consumption in the TPR prole of pure Al 2 O 3 . For different amounts of Pt loaded-g-Al 2 O 3 , reduction peaks were found at a temperature range of approximately 200-400 C. By comparing the reduction peak position and its intensity, we found that the peak position shied to lower values (from 375 C to 216 C) and the intensity increased (approximately 10fold) as the Pt-loading amount increased from 0.6% to 1.0%. The peaks observed below 216 C were mostly attributed to the well-dispersed state of Pt on the Al 2 O 3 support, as well as the reduction of surface oxygen species adsorbed to oxygen vacancies or surface lattice oxygen. 34 In addition, based on the reduction mechanism, the reducing temperature was highly associated with the activity of oxygen species on the catalysts, indicating that the catalysts with low-temperature reducibility would have more active oxygen species. 35 Such results suggested that more active oxygen species could be produced by introducing Pt decoration, which would be benecial for heterogeneous catalytic oxidation reaction, especially at lower temperatures.
In addition, according to the H 2 -TPR spectra of Pt-1.0%/g-Al 2 O 3 before and aer the purication of gaseous cyclohexanone, we found that the reduction peak shied to a much higher temperature of 412 C, which suggested that the active center around Pt was lost aer utilization. 31 3.2 Catalytic activity and stability during cyclohexanone oxidation    temperature, respectively. Fig. 4a shows that the activity of the synthesized catalysts increased with increasing amounts of Pt loading. We also found an abrupt change in the catalytic activity at 190 C for larger amounts of Pt-loading, which was much lower than that observed for Pt-0.6%/g-Al 2 O 3 . Based on these results, proper Pt amounts (0.8-1.0%) might induce higher catalytic activity, but higher Pt loading only increased the catalytic activity over a limited temperature range. Therefore, considering the handling cost and the catalyst's characteristics, Pt-1.0%/g-Al 2 O 3 could be considered as the most suitable catalyst for the catalytic oxidation of cyclohexanone. Catalytic stability is critical for the application of catalytic oxidation. To investigate the long-term activity of the Pt-1.0%/g-Al 2 O 3 catalyst, experiments were performed for up to 250 h, and the results are shown in Fig. 4b. A decrease in cyclohexanone conversion from 100% to less than 80% was observed at 225 h. A deactivation of noble metal catalysts during VOC catalytic oxidation is a common phenomenon. Most frequently, deactivation of noble metal-loaded catalysts is related to metal sintering, transformation of the active metallic oxide to a metal element at higher temperature, or occlusion by the support. 36,37 In this case, to clarify the reasons for the deactivation of the 1.0% Pt-based catalyst, two views were taken into consideration: a change of the BET surface and a temperature shi for the H 2reduction peak. A small difference was observed in the BET surface areas of the catalyst samples before and aer the catalytic tests. For fresh Pt-1.0%/g-Al 2 O 3 , the BET surface area was 150 m 2 g À1 , while for the aged catalyst, the BET surface area decreased to nearly 122 m 2 g À1 . Additionally, the H 2 -TPR data indicated that the aged catalyst had a much higher temperature for the reduction peak. Other studies also found these mostly similar phenomena when they studied catalyst stability. 38,39 Fig. S2 † shows the morphology images of the catalyst before and aer use. The color changed from brown to yellow, which suggested that catalytic intermediates accumulated at the surface of catalysts and catalytically active elements might be gradually lost during the utilization. This phenomenon is similar to that reported in other studies, which showed that coking deactivated catalysts aer long periods of use. 40,41

Optimization of the process parameters by RSM
Several process parameters have a combined effect on catalytic oxidation, and using a single factor may not accurately describe the actual situation. 23 In a xed-bed catalytic-oxidation reactor, the reaction processes are very complex; however, most studies usually focused on the inuence of single process parameter variables on catalytic degradation, and they rarely considered the combined effect by jointly examining the effect of several parameters. In the present study, CCD, 42 the most popular experimental method, was used to obtain the optimal operational conditions for cyclohexanone catalytic oxidation.
Three main parameters, the initial catalyst concentration, the RH, and the GHSV, were chosen. A series of experiments were conducted, and the results of the CCD are shown in Table 3. Through the interactive factors analysis by analysis of variance, we found that the initial catalyst concentration and the GHSV had obvious effects on the catalytic oxidation of cyclohexanone, as did the RH. Additionally, the combined effect of every combination of two factors was obvious, indicating that the interactions between two different parameters were very strong, for example, between the initial catalyst concentration and the GHSV, and between the RH and the GHSV. Not only in  terms of single factors, but also in combination, both the GHSV and RH were more important parameters. The removal efficiency of cyclohexanone decreased with increasing GHSV. A much larger GHSV will remove a large amount of heat, and thus affect the catalytic oxidation efficiency. Meanwhile, a larger RH also had a negative effect on the removal efficiency, since there was competition between the much greater number of H 2 O molecules and the target pollutants in the surface-active sites. All these phenomena could be obtained from the response surface graph and a contour plot between two process parameters, which are supplied in Fig. S3. † A predicted model was obtained from the CCD and RSM analysis and used to demonstrate the relationships among the initial catalyst concentration, the GSHV, and the RH within the range of the tested values. The mathematical model is given below: where A is the initial catalyst concentration (mg m À3 ); B is the GHSV (h À1 ); and C is the RH (%). According to analysis from the RSM model, the maximum conversion efficiency was predicted to be 89.6%, when the initial catalyst concentration, the GSHV, and the RH were 1992.26 mg m À3 , 11 788.84 h À1 , and 47.02%, respectively. A conrmatory test was conducted using an initial concentration of 2000 mg m À3 , a GSHV of 12 000 h À1 , and an RH of 50%, and the actual efficiency was 86.5%, suggesting that the predicted result was in good agreement with the experimental results.

Intermediate distribution and mechanistic analysis
Under the optimal reaction conditions, the oxidation products of cyclohexanone in the effluent were analyzed by GC-MS, and the results are shown in Fig. 5. The results showed that several intermediates, such as benzene, toluene, and cyclopentanone, formed during the catalytic process.
Although the concentrations of some intermediates in the outlet were too low to enable their detection by GC-MS, they might have accumulated on the surface of the catalyst. Therefore, Pt/g-Al 2 O 3 (before and aer use) was analyzed by FTIR. Its spectrum of intermediates is shown in Fig. 5, in which some differences between the curves were observed. A larger peak at a wave number of 3400 cm À1 was observed for the used catalyst, and this peak was identied as OHc. The intensity of a peak at approximately 2900-3100 cm À1 (mainly belonging to CH 3 c or CH 2 c) decreased, suggesting that it might have been oxidized during the reaction. Additionally, some new peaks that were observed at approximately 2400-2300 cm À1 and 700-500 cm À1 might be CO 2 . Peaks at approximately 1900-1000 cm À1 indicated that cyclohexanone derivatives accumulated. Some small aldehydes and carboxylic acids also formed during the catalytic oxidation of cyclohexanone, which might be expressed as the peaks at approximately 1600-1500 cm À1 and 1300-1000 cm À1 , respectively. Based on these FTIR analyses, the main intermediates were alcohols, small-molecule carboxylic acids, aldehydes, carbon dioxide, and cyclohexanone ring derivatives.
Nobel metals for catalytic oxidation may follow two classic mechanisms: the Langmuir-Hinshelwood model (in which all reactants are adsorbed prior to the redox process) and the Eley-Rideal model (in which gaseous hydrocarbon is oxidized directly by the free radical Oc). 17,43 The general mechanism of oxidation using noble metals is considered to involve the dissociative adsorption of oxygen with the formation of a "surface site". Then, the gaseous organic reactant can react directly at these surface sites. However, sometimes the reactant is also weakly adsorbed initially and then oxidized. It has been proposed that catalytic oxidation oen occurs by a parallelseries mechanism. Lattice oxygen, as well as gas-phase oxygen, participates in the catalytic oxidation process, in which [Pt 4+ ] acting as an active redox center plays an important role during the redox cycle. [44][45][46] Based on the detected intermediates and the mechanism of catalytic oxidation, the main degradation pathways of cyclohexanone were proposed, and they are shown in Fig. 6. The removals of cyclohexanone can occur in two possible ways, in which both the dissociative adsorption of oxygen and gas-phase radicals (such as Oc, HO 2 c, and OHc) have the largest effects. Near the surface of the catalyst where oxygen is absent, H-abstraction always played a role during the reaction process.
In the rst way, cyclohexanone is converted via H 2 -abstraction reactions to yield the cyclohexanone radicals R1, R2, and R3. However, these radicals are unstable and might change through a series of rapid reactions, forming 2-cyclohexene-1ketone (for R1, R2, and R3) and C 3 H 5 COC 2 H 5 (for R2 and R3). 47 2-cyclohexene-1-ketone can be attacked directly by the hydroxyl radical, oxygen free radical, and other free radicals, nally forming complete mineralized products (e.g., H 2 O and CO 2 ). The catalytic oxidation of C 3 H 5 COC 2 H 5 is relatively complex. Through ring regeneration, C 3 H 5 COC 2 H 5 is converted to methyl cyclopentyl ketone, and then it is attacked by radicals to form cyclopentanone via a missing methyl radical. Finally, cyclopentanone undergoes ring opening and is further oxidized to form CO 2 and H 2 O. In this study, the intermediates of 2-cyclohexene-1-ketone were not detected, and this pathway was hypothesized based on previous studies. 46,47 In the second way (shown at the bottom of Fig. 6), reduced intermediates (such as benzene, toluene) appeared. It might be that the distribution of oxygen was inhomogeneous in the reaction atmosphere; some places nearly the surface of the catalyst had a lower oxygen concentration (<2%) or no oxygen. Therefore, when both free oxygen and oxygen adsorbed by the catalyst surface were consumed, cyclohexanone underwent a reforming reaction (H-abstraction) that was induced by the active component of catalyst (mainly Pt 4+ ), which produced some reduced intermediates like benzene and toluene. 48 Hydrogen on the benzene ring could be replaced by CH 3 c under special conditions; as a result, benzene was converted to toluene. When toluene and benzene le the surfaces, both these compounds could be attacked by free radicals (such as oxygen free radical), thereby resulting in the formation of benzyl alcohol. Then this compound underwent a series of hydroxylation and oxidation reactions of its aromatic ring, resulting in its conversion to benzaldehyde and benzoic acid. All these intermediates might be easily oxidized to the nal products (CO 2 and H 2 O).
To evaluate the prepared catalyst for the complete removal of cyclohexanone, the amount of CO 2 was measured by a gas chromatograph equipped with a TCD detector. The initial concentrations of cyclohexanone and the GSHV were the same as the obtained optimal values, while RHs were taken at three different ranges. Fig. S4 † shows that both the catalytic oxidation efficiency and mineralized efficiency increased with increasing reaction temperatures. We found that higher RHs (65-75%) had a more negative effect on the mineralization, which indicated that more H 2 O could compete with the reactants and intermediates for the active site on the surface of the catalyst. According to our calculations, the maximum mineralization rate was nearly 80% under a RH of 50%.

Kinetic analysis
To study the kinetics of cyclohexanone catalytic oxidation using Pt/g-Al 2 O 3 , a more sophisticated kinetic model was used as follows: 49,50 where P cyclohexanone and P O 2 are the partial pressure of cyclohexanone and oxygen, respectively; a and b are the reaction orders; k 0 is the kinetic constant; E refers to the activation energy of the reaction; and R is the molar gas constant (equal to 8.314 J mol À1 K À1 ).
To obtain a and b, a series of experiments were conducted under different partial pressures of cyclohexanone and oxygen. The calculated reaction rates are shown in Table 4. Table 4 shows that the partial pressure of cyclohexanone had a decisive inuence on the reaction rate under both high and low temperatures. When the temperature was kept constant, the reaction rate increased with increasing partial pressures, and the increase of the reaction rate at high temperatures was much larger than the one obtained at low temperatures. The effects of oxygen were not greater than 2%. When the catalytic reaction occurred at low temperatures, the oxygen taking part in the reaction might be the adsorbed oxygen on the surface of the active catalyst, and the oxygen coverage would increase slightly with increasing partial pressures; at the same time, the absorbed oxygen would also gradually leave the surface. As a result, the oxygen coverage decreased because the absorbed rate was less than the desorbed one, nally arriving at a lower value when the adsorption and desorption were equal. Therefore, the effect of the partial pressure of oxygen can be ignored, which is to say that b ¼ 0; our results are similar to those of Artizzu-Duart et al. 51 The reaction rate can be written as follows: Using the logarithm method, some parallel lines between ln P cyclohexanone and ln r cyclohexanone were obtained under different temperatures (Fig. 7a). The slopes of these lines were the value of a, 0.31.
To obtain the values of E and k 0 , the logarithm method was also used. Some parallel lines were obtained under different process parameters, with ln r cyclohexanone and ln P cyclohexanone , and ln r cyclohexanone and ln(1/RT) (Fig. 7). Based on these lines, E and k 0 were 52.516 kJ mol À1 and 1.10 Â 10 6 , respectively. These results are very promising because they imply that the modication of g-Al 2 O 3 yielded a very effective synthetic effect, which induced E values that are comparable to those of some noble metal or dual-metal catalysts in the VOC oxidation process. Finally, the reaction rate was obtained as follows: Àr cyclohexanone ¼ 1:10 Â 10 6 exp À6316:58 To determine the accuracy of this model, experiments were conducted, and the results were compared with the values predicted by the model. Fig. 7b shows that the theoretical model was in good agreement with the experimental results, and the relative deviation was less than 3%, with an R 2 of 0.9934. Therefore, the obtained kinetics model for cyclohexanone catalytic oxidation was accurate and credible compared to the actual experimental values.

Conclusions
A platinum-doped g-Al 2 O 3 catalyst was prepared and used for the complete oxidation of cyclohexanone in the present study. A series of characterizations, including TEM, H 2 -TPR, FTIR, and BET, were used to identify the structure and properties of the prepared catalysts. The results showed that nano Pt or Pt oxides formed as the crystalline phase on the Al 2 O 3 support, with a larger surface area for catalytic application. Other experiments revealed that 1.0% Pt-g-Al 2 O 3 had a higher activity for the abatement of cyclohexanone. Through an RSM analysis, the optimal process parameters were obtained, and it was found that the GHSV and RH had much greater interaction effects on the conversion of cyclohexanone. According to the model based on the RSM, the predicted catalytic oxidation efficiency was similar to the experimental value under the optimal operation conditions. A possible conversion pathway was constructed based on the detected intermediates, and the results showed that both the dissociative adsorption of oxygen and gas-phase radicals (such as Oc, HO 2 c, OHc) had effects.
Based on the reaction rates under different partial pressures of oxygen and cyclohexanone, a kinetic model was created with the obtained tting constants, and it accurately predicted the rates of catalytic oxidation. This study provides a possibility for the catalytic combustion of cyclohexanone in industrial applications.

Conflicts of interest
There are no conicts of interest to declare.