pubs.acs.org/EF Article Oxidative Dehydrogenation of n‑Butane to C4 Olefins Using Lattice Oxygen of VOx/Ce-meso-Al2O3 under Gas-Phase Oxygen-Free Conditions Muhammad Y. Khan, Sagir Adamu, Rahima A. Lucky, Shaikh A. Razzak, and Mohammad M. Hossain* Downloaded via WESTERN UNIV on July 8, 2020 at 19:37:29 (UTC). See https://pubs.acs.org/sharingguidelines for options on how to legitimately share published articles. Cite This: Energy Fuels 2020, 34, 7410−7421 ACCESS Read Online Metrics & More Article Recommendations ABSTRACT: High-performance, fluidizable VOx/Ce-meso-Al2O3 catalysts were prepared by an excessive solvent approach. The prepared catalysts were characterized using various physicochemical techniques in order to secure desired properties. XRD, Raman, and FTIR analyses indicated the presence of amorphous VOx phases on Ce-meso-Al2O3. Nitrogen adsorption isotherm analysis confirmed a mesoporous framework with a high surface area of the catalysts. H2-TPR reduction showed an active and stable behavior of the catalysts in repeated reduction and oxidation cycles. The NH3-TPD and NH3 desorption kinetics analysis revealed that the synthesized catalysts have moderate acidities and low activation energies of NH3 desorption, suggesting weak metal−support interactions. The VOx/Ce-meso-Al2O3 catalysts were evaluated for n-butane oxidative dehydrogenation (BODH) using a fluidized CREC riser simulator under gas-phase oxygen-free conditions. The reaction time and reaction temperature were varied between 5 and 25 s and 450−575 °C, respectively. It was found that BODH with 0.2 wt % cerium-doped VOx/meso-Al2O3 catalysts gives the highest selectivity (62.3%) of C4 olefins with a conversion of 10.6% at 450 °C and 5 s. Furthermore, the fluidizable VOx/Ce-mesoAl2O3 catalyst showed a stable performance over repeated feed injections followed by catalyst regeneration cycles for BODH. catalysts stand as good candidates for BODH.9,11−16 However, there are still critical issues related to vanadium catalysts that need to be addressed. For example, the availability of the desired amorphous vanadium oxide species is one of the key aspects for achieving high selectivity of desired C4 olefins.11−16 On the other hand, the support type, vanadium oxide−support interaction, amount of vanadium oxide loading, and method of catalyst synthesis play important roles in achieving highly selective catalysts. It has been shown that high vanadium loadings may yield a nonselective crystalline V2O5 phase for BODH.17 As a result, limited VOx loadings (5−10 wt %) are recommended.18 Similarly, it is reported that the doping of NiMoO4 catalysts with highly basic elements of the IA or IIA groups tends to increase olefin selectivity.19,20 In this respect, it is speculated that the metal−support interactions and the acid−basic nature of the support are key factors affecting C4 olefin selectivity.21 To clarify these matters, nickel oxides and vanadium oxides have been impregnated on the following supports: Al2O3, SiO2, MCM-41, MgO, ZrO2, USY, Ti-HMS, and NaY.12,22−27 Among these materials, magnesium oxide stands as a good support for VOx-based catalysts.28 However, given the need of improving mechanical strength properties for fluidizable catalysts, γ-Al2O3 has been considered as a 1. INTRODUCTION C4 olefins, which include C4 alkenes (1-butene, iso-butene, and cis-butene) and 1,3-butadiene, are important feedstocks for the petrochemical industries. These olefins are processed in the production of variety of polymers and chemicals such as styrene rubber, nitrile butadiene rubber, polybutadiene, polyamides, alkylates, and maleic anhydride.1−3 With the growing world population and improvements in the quality of human life, demands for the aforementioned products/ chemicals (so does the C4 olefins) have increased significantly, which are projected to grow further in the coming years.4 Conventionally, C4 olefins are obtained from various sources, including (i) dehydrogenation of light alkanes, (ii) fluid catalytic cracking of heavy oils, and (iii) hydrocracking of hydrocarbon feedstocks.5 Despite their technical maturity, the conventional processes experience several disadvantages,6−8 such as (i) high-temperature reaction conditions due to the highly endothermic nature of involved reactions, (ii) limitations by thermodynamic constraints and low product selectivity, (iii) severe catalyst deactivation by coke formation, and (iv) energy-intensive product separations. In this regard, C4 olefin production via n-butane oxidative dehydrogenation (BODH) has been considered to be very promising, given the possibility of addressing the issues related to the conventional processes.9−11 Nevertheless, the critical challenge for BODH is to overcome the low yields of the desired C4 olefin products by developing more selective BODH catalysts. Keeping the above into consideration, there are studies in the open literature investigating the various aspects of BODH catalysts. Among the studied catalysts, vanadium oxide-based © 2020 American Chemical Society Received: January 22, 2020 Revised: April 24, 2020 Published: May 1, 2020 7410 https://dx.doi.org/10.1021/acs.energyfuels.0c00220 Energy Fuels 2020, 34, 7410−7421 Energy & Fuels pubs.acs.org/EF preferable support for BODH.29−31 Nevertheless, alumina has a strong acidic character, which leads to low V 2 O 5 dispersions.16 Thus, modification of the γ-Al2O3 support by doping it with group IIA alkaline elements, such as Mg, Ca, Sr, and Ba, has been proposed.12 The effect of the addition of transition metals (Ni, Fe, and Co) on the BiO-γ-Al2O3 support was also investigated as a catalyst modifier.29−31 It was shown that the ternary system (including all-metal species Ni, Fe, and Co) impregnation on the BiO-γ-Al2O3 support improved the selectivity of butadiene reasonably. An increase in catalyst activity was linked to the improved basicity of the alumina support.29 One should, however, notice that this type of γAl2O3 doping remains intrinsically limited given the lack of catalyst stability. Furthermore, the selectivity to the desired C4 olefin products can also be improved by selecting adequate reactor operating conditions. In this regard, BODH under gas-phase oxygen-free conditions could be an interesting alternative to enhance C4 olefin selectivity by suppressing COx formation, which is similar to the ODH of propane (to propylene) and ethane (to ethylene), as demonstrated by the present research group.8,33 This process involves twin interconnected fluidized bed reactors, (i) a ODH reactor and (ii) catalyst regenerator, and solid catalyst particles can be circulated between the fluidized beds. In this approach, the feed n-butane will be dehydrogenated by reacting with the lattice oxygen of the solid metal oxide catalyst. The oxygen-depleted catalyst will be sent to the catalyst regenerator to be reoxidized in contact with air and recycled back to the ODH reactor. Given all the abovementioned facts, a new Ce-doped fluidizable VOx/meso-Ce-Al2O3 catalyst for BODH under gas-phase oxygen-free conditions has been investigated. The proposed catalyst is specially tailored for its dual roles: (i) catalyze the BODH reaction and (ii) act as an oxygen carrier for the BODH reaction. To accomplish this, cerium is used for alumina support modification, which upon oxidation, gives a CeO2 phase. Cerium oxide has outstanding properties to limit support acidity. Also, ceria tends to increase catalyst thermal stability and reduces BODH catalyst deactivation. In this respect, Solsona et al.32 and Khan et al.33 reported improved catalyst activity of NiO and VOx, respectively, due to the incorporation of cerium. It is thus proposed that the vanadium oxide impregnation on cerium-modified alumina in the present study be prepared using the excessive solvent impregnation method.34 It is also considered to characterize the developed BODH catalyst using the following state-of-the-art characterization techniques: XRD, nitrogen adsorption isotherms, TGA, TPR/TPO, NH3-TPD, FTIR, and Raman as well as NH3 desorption kinetics. Finally, the superior BODH catalyst performance for n-butane conversion and C4 selectivity experimental runs were developed in a specially designed fluidized CREC riser simulator under gas-phase oxygen-free conditions. This reactor has the special feature of mimicking the operating conditions of circulating fluidized beds, possible reactor candidates for this BODH process. Article were used without any further purification. Both meso-Al2O3 (MAs) and Ce-meso-Al2O3 (Ce-MAs) catalyst supports were synthesized using the facile free method,35,36 which has also been adopted in our previous work.33,37,38 In the MAs preparation, a 1.0 molar solution of ammonium carbonate was used to partially hydrolyze 0.1 molar solution of aluminum nitrate nonahydrate under continuous stirring. The hydrolysis of the aluminum nitrate solution was continued until a monolithic gel formation was obtained, which was dried at 30 °C for 24 h. Afterward, the dried gel was heated at a rate of 1 °C/min to 150 and 200 °C for 12 h. Subsequently, MAs crystals were calcined at 300 °C at the same heating rate of 1 °C/min for 12 h. Cerium-doped alumina supports (Ce-MAs) were synthesized using the same procedure. However, before the hydrolysis step, an appropriate amount of cerium nitrate solution (yielding 0.2, 1.0, 3.0, and 5.0 wt % Ce in MAs) was added to the aluminum salt solution. The excessive solvent impregnation technique was employed to impregnate 5 wt % vanadium oxide on all synthesized supports. In a typical impregnation of VOx, an appropriate weight of vanadium acetylacetonate salt was dissolved in the excessive volume of toluene under vigorous stirring. The prepared supports (MAs and Ce-MAs) were added to this vanadium salt solution and were allowed to mix under continuous magnetic stirring. After 6 h, the catalyst was separated from toluene in a centrifuge rotating at 4000 rpm. The separated catalyst was then heated to 30 °C for 24 h. The dried sample was then heated (0.5 °C/min) in the furnace at 140 °C for 6 h. The powder catalysts were then reduced in the fluidized conditions using a gas mixture of H2 and Ar in a vertically mounted Thermocraft furnace. Subsequently, the reduced catalysts were calcined in the same furnace at 750 °C for 10 h at a ramping rate of 0.5 °C/min. Table 1 Table 1. Catalyst Designation VOx/Ce-meso-Al2O3 catalyst composition no. wt % V wt % Ce wt % meso-Al2O3 nomenclature 1 2 3 4 5 6 0.0 5.0 5.0 5.0 5.0 5.0 0.0 0.0 0.2 1.0 3.0 5.0 100 95 94.8 94 92 90 MAs 0.0 Ce 0.2 Ce 1.0 Ce 3.0 Ce 5.0 Ce presents the wt % values of different species present in the six different catalysts prepared in the present study. The wt % values shown in Table 1 are determined as per the synthesis method. As we can see, all the cerium-doped catalysts have the same amount of vanadium (5 wt %) over them; hence, they can be named such that they indicate the amount of Ce present in them. For the sake of convenience, we have used the vocabulary of Table 1 throughout this document. For example, the 0.2 Ce acronym represents the 5.0 wt % VOx/0.2 wt % Ce-γ-Al2O3 catalyst. The particle size of all the synthesized catalysts was in a range of 15−110 μm and a Sauter mean diameter of 95 μm. The sizes of the synthesized catalysts are within the range of group A of Geldart’s powder classification, which is similar to commercial fluid catalytic cracking catalysts. 2.2. Catalyst Characterization. The catalysts’ BET (Brunauer− Emmett−Teller) surface areas and pore properties were measured on Quantachrome ASIQwin equipment. In the typical experimental procedure, approximately 150 mg of a catalyst sample was loaded into a U-tube sample holder, and it was preheated under N2 for 3 h at 350 °C. In the adsorption analysis, the bath temperature was maintained at 77 K using liquid N2. The specific surface area was determined using the BET method, and the pore volume and diameter were derived from the BET isotherm using the Barret−Joyner−Halanda (BJH) procedure. X-ray diffraction (XRD) measurements were conducted on a MiniFlex II Rigaku. The equipment is provided with nickel-filtered Cu Kα radiation with a wavelength =0.15406 nm, 15 mA, and 30 kV. The 2. EXPERIMENTAL SECTION 2.1. Catalyst Synthesis. Cerium nitrate hexahydrate (Ce(NO3)3· 6H2O), aluminum nitrate nonahydrate (Al(NO3)3·9H2O), vanadium acetylacetonate, toluene, and ammonium carbonate were used in the synthesis of VOx/Ce-meso-Al2O3 catalysts. The aforementioned chemicals were purchased from Sigma-Aldrich except for ammonium carbonate, which was obtained from Fisher Limited. These chemicals 7411 https://dx.doi.org/10.1021/acs.energyfuels.0c00220 Energy Fuels 2020, 34, 7410−7421 Energy & Fuels pubs.acs.org/EF Article Figure 1. (a) Pictorial view of the main parts of the riser simulator. (b) Schematic diagram of the CREC riser simulator experimental setup.39 °C min−1. The thermal conductivity detector (TCD) was employed to analyze the exit gas composition. Similarly, NH3-TPD measurements help to determine the total acidity of the powdered samples. In all TPD analyses, 100 mg of the calcined catalyst was loaded into the sample holder and was pretreated at 300 °C using He gas for 3 h (30 cm3 min−1). In the subsequent step, the catalyst was heated to 100 °C in a gas mixture of 5% NH3/He at a flow rate of 50 cm3 min−1 for 1 h. The gaseous NH3 molecules were flushed out of the catalyst bed by purging He for an hour at 50 cm3 min−1. NH3 desorption was studied up to 750 °C with a heating rate of 10 °C min−1 under a He flow rate of 50 cm3 min−1. NH3 in the effluent stream was monitored using a TCD detector. Raman spectrums of the synthesized catalysts were determined on a Horiba Raman spectrometer (iHR 320). The apparatus is equipped with a CCD detector that helps to minimize the elastic beam scattering. In a typical experimental procedure, the following settings angle of the incident beams was set between 10 and 90° and a step size of 0.02 with a scanning rate of 3°/min. Thermogravimetric analyses (TGA) were performed on a TA SDTQ600. TGA measurements help in determining the thermal stability of the prepared catalysts. In a typical experimental procedure, 10 mg of the sample was heated at a rate of 10 °C min−1 to 950 °C with a N2 purging flow rate of 100 cm3 min−1. The H2-TPR (temperature-programmed reduction) and NH3-TPD (temperature-programmed desorption) experiments were conducted on a Micromeritics (AutoChem-II) apparatus. Along with the redox properties, TPR/TPO analyses also help in evaluating the catalyst stability. In each experimental run, an equal amount of the catalyst sample (100 mg) was placed in the quartz U-tube. Before the reduction step, the samples were pretreated in argon (99.9%) at 300 °C for 3 h (50 cm3 min−1). A gas mixture of 5% H2/Ar (50 cm3 min−1) was used for the reduction at 850 °C at a ramping rate of 10 7412 https://dx.doi.org/10.1021/acs.energyfuels.0c00220 Energy Fuels 2020, 34, 7410−7421 Energy & Fuels pubs.acs.org/EF were used: excitation λ = 532 nm and laser intensity = 50% at 50− 2500 spectrums. Before the collection of spectrums, each catalyst was dehydrated for 1 h at 500 °C. 2.3. Reactor System. The n-butane ODH (BODH) reactions were carried in the fluidized bed CREC riser simulator using only the lattice oxygen of the catalyst. This mini-batch reactor has a 53 cm3 reaction volume and is specially designed to investigate the ODH catalyst’s activity and reaction kinetics in a fluidized condition (riser/ downer).39 The reactor is shown in Figure 1, illustrating that the reactor has two major sections: (a) the upper part and (b) the lower part. The complete reactor assembly includes the following principal parts: grids, impellers, heaters, retaining rings, thermocouples, and cooling jackets. The reactor is connected to the vacuum chamber via an automatic four-port valve that directs the reaction products to be collected to the vacuum chamber. An online GC−MS was connected to the vacuum chamber through a six-port valve to analyze these reaction effluents.22,40 In all the BODH experiments, 1.0 g of the synthesized catalyst was loaded into the reactor. Prior to each run, the reactor and vacuum chamber were purged with Ar gas for 15 min, and a leak test was conducted. Then, the leakproof reactor’s temperature was increased in a stepwise manner to a desired reaction temperature value under continuous flushing with Ar gas to eliminate hot spots and the atmospheric gas-phase oxygen interface. Upon reaching the temperature set point, the reactor was degassed to 1 atm pressure using a vacuum pump. Finally, the reaction vessel was disconnected from the vacuum chamber with the help of an isolation valve. In the following step, the vacuum chamber pressure was further decreased to 0.26 atm using a vacuum pump. Before the BODH reactions, the catalyst bed was fluidized using an impeller rotating at a speed of 5000 rpm. All BODH experiments were performed in the fluidized bed condition with no gas-phase oxygenthis is to make sure that only the lattice oxygen of the catalysts is used. It is possibly important to mention here that the intense mixing of the small catalyst particles (15−110 μm) and gaseous n-butane (feed) eliminates any possibility of mass transfer limitations. The BODH reactions were studied in a temperature range of 450−600 °C, and the resident time was varied within 5−25 s. The reactor temperature was gradually raised from the ambient temperature to the desired temperature value under a continuous flow of Ar. After each experimental run, the spent catalyst was oxidized with zero air at 575 °C for 10 min, and upon completion of the regeneration step, the supply of air was stopped. Subsequently, the reactor was cleaned with argon gas for 15 min. The pure n-butane (99.97%) is used as a feed in all BODH experiments. All experiments were performed at a pressure = 1 atm, impeller speed = 4000 rpm (used for fluidization), and feed-to-catalyst ratio = 1 mL of n-butane/ 1.0 g of catalyst. One milliliter or the equivalent of 2.48 mg of pure nbutane was then fed into the reaction chamber via a preloaded airtight syringe. Upon the completion of the reaction, a valve automatically connected the reactor with the vacuum chamber. Thus, this allowed the reaction effluents to be analyzed by an online GC (Agilent 7890A) equipped with FID and TCD detectors. After each BODH reaction, the used catalyst was reoxidized at 575 °C for 10 min using zero air. The products of n-butane ODH (BODH) reaction were identified using an online GC. Further computation with the GC results enables us to calculate conversion (X) and selectivity (Si) with the help of the following formulas: i moles of feed reacted yz zz × 100 conversion, X (%) = jjj k moles of n − butane fed { Article desorption isotherms of the bare calcined meso-Al2O3 support and 0.2 Ce and 1.0 Ce catalysts are displayed in Figure 2. The Figure 2. N2 adsorption isotherms of bare MAs, 0.2 Ce, and 1.0 Ce samples. complete nitrogen adsorption isotherm analysis, namely, BET surface area, BJH pore size, and pore volume, are given in Table 2 with a cross-correlation coefficient value of >0.99 and Table 2. BET Surface Area, Pore Volume, and Pore Size of the Bare Support catalyst SBETa (m2/g) VBJHb (cm3/g) rBJHc (nm) MAs 0.0 Ce 0.2 Ce 1.0 Ce 3.0 Ce 5.0 Ce 296 231 152 142 99 88 0.8 0.6 0.4 0.4 0.3 0.2 10.2 9.3 8.4 5.6 4.2 3.6 a SBET, surface area of the catalyst bVBJH, pore volume crBJH, average pore width 95% confidence interval. All the analyzed samples showed a type IV isotherm, assigned to the mesoporous materials that typically form a monolayer, which is followed by the multilayers, finally resulting in the capillary condensation that starts at a relative pressure of ∼0.6. The surface area of the calcined meso-Al2O3 catalyst support was found to be 296.5 m2g−1, which is within the range of surface area as reported in the literature35,36 and consistent to the value that the authors found in previous works.33,34,37 As can be observed in Table 2, the surface area of the bare MAs decreases from 296.5 to 88.4 m2g−1 for the 5.0 Ce catalyst. Therefore, with an increase in cerium wt % and an overlayer of vanadium in the catalyst matrix, the BET surface area, BJH pore width, and BJH pore volume of all the samples decrease. Thus, more highly doped catalysts will have a smaller BET surface area. This adverse effect is due to the breakdown and blockage of the MAs pores, which are due to the presence of dopant (cerium) and impregnated overlayer of VOx. The average pore sizes of the MAs (meso-Al2O3 support) and all other catalysts are in a range of 2−50 nm, which according to IUPAC nomenclature, is classified as mesoporous.41 The BET analysis has confirmed the formation of the high surface area of mesoporous catalysts. (1) i moles of product i yz zzz × 100 selectivity of product i, Si (%) = jjjj k moles of feed reacted { (2) 3. RESULTS AND DISCUSSION 3.1. Catalyst Characterizations. 3.1.1. Nitrogen Adsorption Isotherm Analysis. As a reference, the adsorption/ 7413 https://dx.doi.org/10.1021/acs.energyfuels.0c00220 Energy Fuels 2020, 34, 7410−7421 Energy & Fuels pubs.acs.org/EF Article This could be related to the excellent performance of the catalysts in ODH reactions. 3.1.2. X-ray Diffraction. The XRD patterns of the prepared support and catalysts are shown in Figure 3. The XRD patterns Figure 4. TPR profiles of the freshly prepared catalysts with varying amounts of dopant wt %: (a) 0.2 Ce, (b) 1.0 Ce, (c) 3.0 Ce, and (d) 5.0 Ce samples. Figure 3. XRD patterns of MAs, 0.0 Ce, 0.2 Ce, 1.0 Ce, 3.0 Ce, and 5.0 Ce samples. of CeO2 in γ-Al2O3 also inhibits the transformation of the γAl2O3 phase to α-Al2O3 phase.46 The H2-TPR profile for the calcined 0.0 Ce catalyst (0.0 wt % Ce, 5.0 wt % V, and 95.0 wt % γ-Al2O3) showed only one asymmetric peak extending from 270 to 475 °C. The reduction observed in the preceding temperature range is assigned to the monomeric and polymeric reduction of the amorphous VOx with the oxidation states of V+5 and V+4, respectively.8 A similar observation of VOx reduction in a temperature range of 280−500 °C was also reported by Reddy and Varma,47 Martinezhuerta et al.,48 and our previous articles.33,47,48 The cerium-doped 0.2 Ce, 1.0 Ce, 3.0 Ce, and 5.0 Ce catalysts also displayed low-temperature H2-uptake peaks. However, due to the presence of both VOx and CeO2 phases (as seen in XRD), the TPR peak at low temperatures is assigned to the reduction of both VOx and CeO2 phases. The contribution of CeO2 in the consumption of H2 is because of the surface reduction of the CeO2 phase having an oxidation state of Ce+4, as also observed by Kaŝpar et al.49 Furthermore, the temperature of the maximal H2-TPR consumption (Tmax1) has increased with the amount of cerium (dopant) in the support. The increase in reduction temperature is believed to be due to the formation of stable monomeric surface species.50 The TGA analysis also exhibited a similar trend where higher-cerium-containing (3.0 Ce and 5.0 Ce) catalysts showed more excellent thermal stability.51 Furthermore, in XRD characterizations, 3.0 Ce and 5.0 Ce catalysts showed intense diffraction peaks for the CeO2 phase. The reduction at high temperatures with the maximum at 800 °C is solely attributed to the bulk reduction of the CeO2 phase, which is only noticeable in 3.0 Ce and 5.0 Ce catalysts, as presented in Figure 4. The catalyst reduction at high temperatures shows a strong metal−support interaction.51,52 This high-temperature reduction peak is absent in both 0.2 Ce and 1.0 Ce catalysts due to a very low Ce concentration (CeO2) in these catalysts.33 However, as the loading of cerium increases, so does the formation of the crystalline CeO2 phase, as previously confirmed by XRD analysis. The increase in CeO2 formation results in the high-temperature H2 consumption peak. of the bare MAs exhibit peaks at 2θ = 37.0°, 45.5°, and 67.0°, corresponding to mesoporous γ-Al2O3 (JCPDS 10-0425).35 The modification of MAs with different cerium wt % values leads to a change of intensity and shape of XRD peaks of γAl2O3, except for the 0.2 Ce catalyst. As evident in Figure 3, no diffraction lines for the crystalline CeO2 phase were noticed for the 0.2 Ce catalyst (0.2 wt % cerium-doped catalyst), suggesting the amorphous CeO2 phase formation at a low loading of cerium. With increasing the cerium loading beyond 0.2 wt %, the intensity of the cerium oxide diffraction lines also increased. According to JCPDS 34-0394, the diffraction lines at 2θ = 28°, 33°, 47.2°, 56.1°, 58.5°, 76.5°, and 79.0° are the characteristic spectrum of the cubic crystal structure of the CeO2 phase.42 At a higher loading of cerium (>3.0 wt %) in the catalyst, the diffraction peaks corresponding to the ceria phase become well resolved and sharper. The presence of the intense peaks of CeO2 at higher loadings, i.e., 1.0 Ce, 3.0 Ce, and 5.0 Ce, decreases the intensity of the main lines of the γAl2O3 support at 2θ = 37.0° and 45.5°.43 Meanwhile, no diffraction lines were observed for crystalline VOx (besides MAs, every catalyst is impregnated by 5 wt % vanadium; Table 1), suggesting either crystalline VOx particles are very small (size of ≤3 nm) and highly dispersed or there is amorphous VOx phase formation.8,44,45 This will be further discussed in section 3.1.6 of this article (Raman spectroscopy). Finally, no diffraction peaks were observed for AlV3O9, which means that the prepared catalysts are free of solid solution formation between VOx and MAs, or we can say that there is no solid reaction between the VOx and MAs. 3.1.3. Reduction of Catalysts by H2-TPR. The H2-TPR profiles of the calcined samples with different loadings of cerium (0, 1, 2, 3, and 5 wt %) are depicted in Figure 4. According to the TPR peaks of the catalysts in Figure 4, 0.0 Ce, 0.2 Ce, and 1.0 Ce catalysts showed only one broad lowtemperature H2 reduction peak in a temperature range of 270− 475 °C, while 3.0 Ce and 5.0 Ce catalysts also showed a hightemperature H2 uptake peak centering at 800 °C. The presence 7414 https://dx.doi.org/10.1021/acs.energyfuels.0c00220 Energy Fuels 2020, 34, 7410−7421 Energy & Fuels pubs.acs.org/EF Article The detailed parameters of the maximum reduction temperature and total H2 consumption are illustrated in Table 3. The low-temperature H2 consumption peaks were Table 3. H2 Consumption of Calcined Catalysts with Different wt % Values of Cerium (0.0, 0.2, 1.0, 3.0, and 5.0) low-temperature samples reduction (Tmax1, °C) 0.0 0.2 1.0 3.0 5.0 Ce Ce Ce Ce Ce 424.0 430.0 456.5 463.6 473.8 high-temperature reduction (Tmax2, °C) total H2 consumption (cm3 g−1) 796.5 797.0 39.2 35.8 44.3 45.0 48.37 located between 270 and 475 °C, while the higher-temperature reduction peaks were centered at ∼802 °C. The total H2 consumption for all the synthesized catalysts is the summation of reductions by VOx and CeO2 phases except for the 0.0 Ce catalyst. The complete H2 oxidation of 0.0 Ce, 0.2 Ce, and 1.0 Ce is almost comparable due to the presence of the same loading of VOx (5 wt %) on each cerium-modified support. However, the highly doped catalysts (3.0 Ce and 5.0 Ce) also result in the secondary high-temperature reduction peak, which contributes to more H2 uptake. As previously discussed, H2 consumption at this temperature is due to the bulk reduction of the CeO2 phase, and from a BODH perspective, the high percentage of CeO2 is generally unfavorable as it is reported to promote the complete combustion reactions (CO and CO2).53 The total H2 consumption values given in Table 3 are the average of the five repeated reduction cycles. All the catalysts showed a higher H2 consumption during the first cycle of the reduction, and this is because of a decrease in nitrate species on the freshly prepared catalysts that tends to increase the H2 consumption. However, with the completion of the first cycle of reduction, the surface nitrate species are eliminated; thus, the H2 uptake becomes constant in the rest of the TPR cycles. Thus, one can predict that 5.0 Ce will be more reactive (will give the highest HC conversion), but because of the presence of a high percentage of easily reducible CeO2 species, it may not be selective for olefin production. 3.1.4. NH3-TPD Analysis. It is generally believed that olefin selectivity in the ODH reaction mainly depends on the overall acidity of the catalysts.54,55 NH3-TPD was thus employed to calculate the total acidity and metal−support interactions. NH3 is widely used for the determination of the aforementioned properties because of its smaller size and a wide range of temperature applications.56 The effect of cerium doping on the overall acidity of the VOx/γ-Al2O3 catalysts can be viewed via NH3-TPD profiles, displayed in Figure 5. The typical values of maximal desorption temperatures and total acidity of all samples are summarized in Table 4. The acidic sites are classified into three main categories (weak, medium, and strong) based on the maximal desorption temperature.57,58 All the tested samples showed an initial broad low-temperature desorption peak at around 195 °C, which is attributed to NH3 desorption from weak acid sites, whereas a high-temperature desorption peak at ∼544 °C indicates the NH3 adsorbed on acidic sites with strong acidic strength. The synthesized γ-Al2O3 support showed a total acidity of 11.4 cm3 g−1, while the acidity of the unmodified VOx/γ-Al2O3 (0.0% Ce) catalyst was found to be 13.1 cm3 g−1, which is due Figure 5. NH3-TPD profiles of 0.2 Ce, 1.0 Ce, 3.0 Ce, and 5.0 Ce. Table 4. NH3-TPD Analyses of MAs and 0.0 Ce, 0.2 Ce, 1.0 Ce, 3.0 Ce, and 5.0 Ce total acidity catalysts (cm3 NH3/g cat) γ-Al2O3 0.0 Ce 0.2 Ce 1.0 Ce 3.0 Ce 5.0 Ce 11.4 13.1 7.6 8.1 10.1 10.7 maximum desorption temperature for weak acid sites (°C) maximum desorption temperature for strong acid sites (°C) 200 196 200 196 193 192 395 550 547 543 542 to the acidic nature VOx (Table 4). However, the total acidity of cerium-modified catalysts (0.2 Ce, 1.0 Ce, 3.0 Ce, and 5.0 Ce) was found to be lower than those of both bare γ-Al2O3 and VOx/γ-Al2O3. A similar trend of increasing acidity of the alumina support upon impregnation of VOx has previously been reported by Al-Ghamdi and de Lasa8 and Datka et al..59 The total acidity of the 0.2 Ce catalyst is 7.64 cm3 g−1; in comparison with the 0.0 Ce catalyst, the presence of cerium in the catalyst has significantly reduced the overall acidity of the VOx/Ce-γAl2O3 catalyst. However, a further increase in the loading of cerium to 1.0 wt % slightly increases the total acidity, but still the acidity is lower than those of the bare support (γ-Al2O3) and cerium-free VOx/γAl2O3 catalyst (0.0 Ce). The slight increase in acidity upon addition of cerium is assigned to the synergetic effect of both CeO2 and VO2 phases, promoting more strong acidic sites in comparison to weak acidic sites, which is reflected by the significant shift of the high-temperature peak (also the area under the curve). This is in agreement with our previous work33 and was also observed by Wu et al.60 and Lee et al.,61 suggesting that a higher loading of cerium creates new strong acidic sites on the support’s surface and increases the overall acidity. 3.1.5. NH3-TPD Kinetics. The activation energy (Edes) and the pre-exponential factor (kdesO) of NH3 desorption were determined by fitting the NH3-TPD data into the kinetics model. The knowledge of Edes and kdesO is essential to understand the metal−support interaction and ease of product (C4 olefin) desorption from the catalyst pores, respectively. The estimated kinetics parameters are applicable under the following assumptions: the single activation energy of desorption (Arrhenius equation) and Edes are independent of 7415 https://dx.doi.org/10.1021/acs.energyfuels.0c00220 Energy Fuels 2020, 34, 7410−7421 Energy & Fuels pubs.acs.org/EF abundant amount of lattice oxygen,45 making them potentially more active for the reactions (higher conversion in BODH). However, at a much higher loading of cerium, the catalysts will become less selective toward BODH reactions due to more loosely bound lattice oxygen and higher acidity.66 On the other hand, the catalysts having less cerium wt % (0.2 Ce and 1.0 Ce) require greater energy to desorb NH3, showing relatively stronger metal−support interactions than the one having a higher cerium wt % (3.0 Ce and 5.0 Ce). These make them, in turn, less reactive but highly selective for the BODH reaction (higher olefin selectivity). Sedor et al. have also demonstrated a similar trend for the Ni/Al2O3 catalysts, which is the fact that a catalyst having a small amount of metal oxide results in higher activation energy, which corresponds to a strong metal− support interaction.40 It must be pointed out that these TPD kinetics modeling results agree with the TPR characterization, which showed higher reactivity for the catalysts with more cerium wt %, resulting in a higher H2 uptake (see Table 3). XRD characterization also agrees with the NH3-TPD results by presenting sharp peaks of CeO2 for 3.0 Ce and 5.0 Ce catalysts (see Figure 3). According to Trovarelli, the higher concentration of CeO2 wt % in the catalyst, the greater the availability of the lattice oxygen.46 3.1.6. Raman Spectroscopy. Figure 6 reports the Raman spectrum of the synthesized catalyst in the range of 100−1200 the surface coverage of adsorbates; there is a uniform distribution of NH3 concentration over the catalyst bed; NH3 desorption from the catalyst surface is governed by the second-order rate process; the desorption process is irreversible (no readsorption); molecular transport and convection transport resistances are negligible; and the catalyst bed temperature increases linearly with time.60,62 NH3-TPD experiments were performed by considering the aforementioned assumptions. The desorption constant (Kd) is given by Arrhenius’ eq 3. By performing an ammonia balance across the catalyst bed and after mathematical simplifications, the rate of desorption (rdes) is given by eq 4 i −E y Kd = kdesO expjjj des zzz k RT { (3) ij −E ij 1 i dθ y 1 yzyz n rdes = −Vmjjjj des zzzz = kdesO θdes expjjjj des jjj − zzzzzzz j Tn z{{ k dT { k R kT and (4) The change in volume of desorbed NH3 with respect to temperature can be obtained as63,64 2 ij E ij 1 kdesO ijj Vdes yzz ij dVdes yz 1 yzyz jj zz = jjj1 − zzz expjjjj− des jjjj − zzzzzzzz β k Vm { Tn {{ k dT { k R kT Article (5) where θdes, Vm, Tn, n, and β represent the catalyst surface coverage, monolayer volume, centering temperature, order of desorption process, and heating rate, respectively. Equation 5 was fitted to experimental data by a NonlinearModelFit builtin function in Mathematica. All NH3-TPD data were obtained using a catalyst mass = 0.1 g and β = 10 °C min−1. The desorption parameters given in Table 5 were estimated with a correlation constant value (R2) > 0.99, confidence interval = 95%, degree of freedom = 3769, and large negative Akaike Information Criterion (AIC) value. Table 5. Estimated Kinetics Parameters at a Heating Rate of β = 10 °C min−1 samples 0.0 0.2 1.0 3.0 5.0 Ce Ce Ce Ce Ce Edes (kJ/mol) R2 AIC Vdes (mL/g cat) ± ± ± ± ± 0.99 0.99 0.99 0.99 0.99 −46,361 −45,379 −41,149 −44,664 −38,882 13.1 7.6 8.1 10.1 10.7 28.0 19.7 14.3 11.6 11.3 0.1 0.1 0.1 0.1 0.1 Figure 6. Raman spectrums of MAs, 0.0 Ce, 0.2 Ce, 3.0 Ce, and 5.0 Ce catalysts. cm−1. The absence of Raman peaks for MAs is because of the ionic characteristic of the Al−O bond.67 The VOx spectrum not only is a function of the vanadium loading but also depends on the type and concentration of the surface species. In the 0.2 Ce catalyst, the only weak band is detected at 1130 cm−1. This spectrum of VOx at 1130 cm−1 is almost invisible in the 0.0 Ce catalyst. The transmittance in the 1130 cm−1 region is assigned to the widely spread surface species of monovanadate with an isolated tetrahedral geometry. The 3.0 Ce and 5.0 Ce catalysts also exhibit a similar Raman band at 1130 cm−1 but with a much higher intensity of the line. The 5.0 Ce catalyst also shows the second Raman band in 950 cm−1 due to the V−O−V bond, suggesting crystalline V2O5 phase formation. However, no XRD lines were detected for V2O5 crystals, possibly due to their tiny sizes. Thus, the 5.0 Ce catalyst showed the presence of both polyvanadate and monovanadate surface species.17 Raman spectroscopic analysis In Table 5, lower desorption energies for all cerium-doped catalysts (0.2 Ce, 1.0 Ce, 3.0 Ce, and 5.0 Ce) are noticed as compared with the cerium-free catalyst (0.0 Ce). Furthermore, the calculated desorption energies are also lower than those reported in the literature by Bakare et al. for VOx/γ-Al2O3 catalysts.45 The lower desorption energies mean that less energy is required to desorb the absorbed NH3 molecules from the catalyst’s pores, suggesting weaker metal−support interactions. The estimated desorption energies in the present study lie between the range reported in the literature.45,64,65 In comparison to the 0.0 Ce catalyst, cerium-doped catalysts generally will be more selective for the BODH because it will easily desorb the olefins. The catalysts with more cerium wt % (3.0 Ce and 5.0 Ce) relatively require the least activation energy for desorption, which in turn corresponds to the 7416 https://dx.doi.org/10.1021/acs.energyfuels.0c00220 Energy Fuels 2020, 34, 7410−7421 Energy & Fuels pubs.acs.org/EF Article is in complete harmony with XRD analysis (see Figure 3) and H2-TPR experiments (see Table 3). The increase in cerium loading in the catalysts reduces the dispersion of the VOx that promotes the formation of the VOx crystalline phase. The Raman spectrum for the CeO2 phase appeared at 460 cm−1 wavenumbers, and the intensity of the CeO2 line increases with cerium wt % in the catalyst; a good resolve peak can be easily seen in the spectra of 3.0 Ce and 5.0 Ce catalysts. The band at 460 cm−1 corresponds to the CeO2 phase with a fluorite structure, which was also confirmed by the XRD characterization (see Figure 3).68 3.2. ODH in the CREC Riser Simulator. Prior to the actual BODH experiments, different thermal runs were conducted to determine the possible contribution of pyrolysis to the total yield of desired products. These blank runs were performed on the empty reactor at 10 s residence time and within the temperature range of 450−600 °C. Figure 7 Figure 8. Effect of cerium loading on n-butane conversion, C4 olefin selectivity (including all the isomers, iso-butylene, 1-butene, 2-butene, etc.), and COx selectivity at 500 °C (standard deviation within ±2.5% of replicate experiments (w = 1.0 g, feed = 1 mL, t = 10 s)). the 0.2 Ce catalyst (50.2%). The lower C4 olefin selectivity over the 0.0 Ce (5.0 wt % VOx/γ-Al2O3) catalyst is mainly due to its higher acidity, which promotes cracking reactions. On the contrary, the 0.2 Ce catalyst had previously shown the least acidic nature (see Table 4), so it minimizes the cracking reactions and, in return, promotes C4 olefin selectivity. That is why a higher C4 olefin yield is observed over the 0.2 Ce catalyst (7.7%) as compared with the 0.0 Ce catalyst (6.2%). Among the Ce-promoted VOx/Ce-γ-Al2O3 catalysts, the highest C4 olefin selectivity of 50.2% with 15.4% conversion is obtained by the 0.2 Ce catalyst (0.2 wt % cerium-doped VOx/ γ-Al2O3). With a further increase in cerium content, there is both an augmented n-butane conversion and COx selectivity. One can also notice a trend toward lower C4 olefin selectivity at a higher amount of cerium-containing catalysts. For example, the 5.0 Ce catalyst showed the lowest C4 olefin selectivity of 30.1% with the highest n-butane conversion of 22%. Figure 8 results can be supported using both TPD and TPR characterization data. TPR demonstrates that higher CeO2 leads to more reducible species on the surface of the catalyst and higher lattice oxygen availability (as shown in Table 3 with the higher H2 uptake). The higher H2 consumption means more reactivity. Also, TPD provides lower desorption energies, suggesting less metal−support interactions, making them more reactive for n-butane conversion. That is why a higher conversion is observed on 5.0 Ce and 3.0 Ce catalysts as compared to 0.2 Ce and 1.0 Ce catalysts. Raman and XRD analyses revealed a greater concentration of the CeO2 phase on 5.0 Ce and 3.0 Ce catalysts. The contact of these catalysts with n-butane results in the formation of more COx because of the easily reducible CeO 2 phase, which favors complete combustion reactions. Similarly, trends of lower alkane selectivity with higher loadings of cerium have also been reported by Martin et al.,19 Maldonado-Hodar et al.,20 and Xu et al.12 The higher-cerium-containing catalysts have revealed higher acidity (see TPD Table 4), which favors the cracking reactions and gives <C4 hydrocarbons (HC). Once <C4 HC have formed, these degraded fractions react in an unselective manner with the lattice oxygen and result in the formation of Figure 7. n-Butane conversion vs temperature for thermal blank runs (standard deviation within ±2.5% of replicate experiments (w = 1.0 g, feed = 1 mL, t = 10 s)). illustrates a direct correlation between n-butane conversion and reaction temperature, provided that the reaction is performed anaerobically. The lower conversion values (<3.5%) depicted in Figure 7 suggest that pyrolysis of nbutane would have a negligible effect on BODH reactions. In particular, also for a selected temperature of 450 °C and reaction time of 10 s, it was noticed that the thermal n-butane conversion was limited to 1.2%. Therefore, based on the thermal blank runs, n-butane conversion in the BODH reactions will solely be attributed the VOx/Ce-MAs catalysts. Figure 8 reports the effect of cerium loading on VOx/Ce-γAl2O3 performance under anaerobic conditions at 500 °C and 10 s. It can be observed that the 0.0 Ce (VOx/γ-Al2O3) catalyst gives a 17.4% n-butane conversion with a 35.5% C4 olefin selectivity (including all the isomers, iso-butylene, 1-butene, 2butene, etc.) and 42% COx selectivity. Coke was not considered in selectivity calculation because of its minimal concentration. The availability of oxygen in the catalyst helps to minimize coke formation.45 It appears that the 0.0 Ce catalyst shows a slightly higher n-butane conversion (2%) than the 0.2 Ce catalyst, which is due to a higher BET surface area of this catalyst (230.8 m2 g−1). However, C4 olefin selectivity of the 0.0 Ce catalyst is significantly lower (35.5%) than that of 7417 https://dx.doi.org/10.1021/acs.energyfuels.0c00220 Energy Fuels 2020, 34, 7410−7421 Energy & Fuels pubs.acs.org/EF more COx.12,19,20 The indirect formation of COx on 5.0 Ce and 3.0 Ce catalysts also contributes to higher COx selectivity. On the other hand, the catalysts containing lesser cerium (0.2 Ce and 1.0 Ce catalysts) have strong metal−support interactions, as shown by the small uptake of H2 and higher desorption energy (see TPD kinetics Table 5), suggesting lower conversion due to more compactness for lattice oxygen.8,9,17 However, higher C4 olefin production on 0.2 Ce and 1.0 Ce catalysts is again due to lower acidity (less formation of <C4 HC) and more selective surface oxide species.66 Based on the highest C4 olefin yield/selectivity observed on the 0.2 Ce catalyst, as revealed in Figure 8, only the 0.2 Ce catalyst will be investigated in the subsequent part of the present study. The typical product distribution for the BODH over the two extreme conditions of the temperature (450 and 600 °C) on the 0.2 Ce catalyst is shown in Figure 9. The BODH products Article Owens, Owen et al., Patel and Andersen, and Armendariz et al.16,66,69,70 Therefore, the elevated reactor’s temperature makes both n-butane and C4 olefins more vulnerable to form cracking products (<C4 hydrocarbons), which upon complete oxidation, result in COx.71 The performance of the 0.2 Ce catalyst is further assessed by studying the effect of residence time on the selectivity of C4 olefins, keeping constant reaction temperatures (450 °C and 550 °C), as shown by Figure 10. A similar trend is noted, as Figure 10. C4 olefin selectivity and n-butane conversion vs reaction time at various reaction temperatures (deviation within ±2.5% of replicate experiments; w = 1.0 g, feed = 1 mL). previously represented by the effect of temperature on product selectivity (see Figure 9). Although C4 olefins are the main reaction product, their selectivity decreased significantly with an increase in contact time. At a reaction time of 5 s and 450 °C, the maximum selectivity of 62.4% is obtained for C4 olefins; whereas, the 25 s and 550 °C reaction conditions give the lowest C4 olefin selectivity of 28.1%. We can conclude that long residence times favor conversion of the feed; that is, the longer contact time of the hydrocarbons with the lattice oxygen of the catalyst, the higher the concentration of byproducts (COx and <C4 hydrocarbons). A similar trend is also reported by Volpe et al. and Cavani et al. that at long residence times, there is more possibility of direct and indirect complete combustion of n-butane and C4 olefins, respectively.22,72 It is obvious that the selectivity of COx follows the reverse trend (higher concentration COx at higher residence time), as compared with the selectivity of C4 olefins. It was found in the present study that elevated reaction temperatures and longer residence contact times favor the COx formation. As mentioned before, this is because of an increase in the rate of (1) direct complete oxidation of n-butane, (2) combustion of formed C4 olefins to COx, and (3) indirect formation of COx by complete oxidation of cracked products (<C4 HC) with the unselective lattice oxygen of the catalyst. Figure 11 illustrates four successive BODH reactions performed at the same operating conditions (residence time = 5 s, temperature = 450 °C, and catalyst = 0.2 Ce). As in BODH reactions, only the lattice oxygen of the catalyst is consumed; therefore, after each experimental run, the spent catalyst was regenerated (oxidized in air at 575 °C for 10 min), which is used for subsequent BODH runs. These experiments are important as they demonstrate the reproducibility of results and, hence, the consistent nature of catalysts. Previously, the Figure 9. Typical product distribution of BODH reaction at 450 and 600 °C over 0.2 Ce (standard deviation within ±2.5% of replicate experiments (w = 1.0 g, feed = 1 mL, t = 10 s)). include methane, ethane, ethylene, propane, propylene, COx, and C4 olefins, while it is clear that C4 olefins and COx (CO + CO2) are the main reaction products. Figure 9 illustrates the negative effect of reaction temperature on the selectivity of C4 olefins. This is a typical trend in BODH reactions, as stated by Madeira and Portela that low temperatures result in higher olefin selectivity.6 We have also noticed a similar behavior in which a low temperature corresponds to a lower feed conversion but results in higher selectivity of C4 olefins. Therefore, we can conclude, as said in previous literature, that a low reaction temperature favors olefin formation over the 0.2 Ce catalyst. However, at high reaction temperatures, exactly an opposite trend was observed. An elevated reaction temperature supports the feed conversion at the expense of olefin selectivity. As seen in Figure 9, the higher n-butane conversion at 600 °C contributes more toward COx and cracking product (<C4 hydrocarbons) formation, indicating that higher reaction temperatures make catalysts more selective for unwanted products (COx and <C4 hydrocarbons).9 The reason for higher conversion is because of the more activation of C−H bonds of n-butane and C4 olefins, which results in a higher concentration of COx and degradation products in the effluent stream. This behavior has also been reported by Kung and 7418 https://dx.doi.org/10.1021/acs.energyfuels.0c00220 Energy Fuels 2020, 34, 7410−7421 Energy & Fuels pubs.acs.org/EF 520 °C displaying a 56% C4 olefin selectivity at a 5% n-butane conversion in a fixed-bed reactor under a gas-phase oxygen-free environment.27 Comparable selectivity results were achieved by Lemonidou et al.,73Rubio et al.,75 Dejoz et al. using magnesium-based catalysts.76 It is however argued that in order to achieve a stable BODH catalytic process, its implementation in circulating fluidized beds requires a limitation on the catalyst flow. Table 5 shows that the VOx/Ce-γAl2O3 (0.2 Ce) catalyst of the present study achieves at 450 °C a 62.4% C4 olefin selectivity at a 10.7% nbutane conversion. The promising performance is accomplished under gas-phase oxygen-free conditions and low coke formation (less than 1.3 wt %). Thus, this BODH catalyst displays great stability under repeated n-butane injections. This commendable activity of BODH at 450 °C, confirmed using TPR analysis, can be assigned to the high catalyst specific surface area and high density of active sites. As a result, this BODH catalyst appears to be very suitable for continuous circulating fluidized operation at 450 °C, with minimal catalyst regeneration in between BODH cycles. Figure 11. C4 olefin selectivity and n-butane conversion for successive BODH with interstage catalyst reoxidation over 0.2 Ce (standard deviation within ±2.5% of replicate experiments (w = 1.0 g, feed = 1 mL, T = 450 °C, t = 5 s)). 4. CONCLUSIONS The effect of cerium doping on fluidizable VOx/γ-Al2O3 catalysts was investigated both using surface science characterization and the gas-phase oxygen-free BODH in a CREC riser simulator batch reactor. The following are the main findings: (i) BET analysis revealed a mesoporous framework with a high specific surface area. An inverse relationship between the specific surface area and cerium content was also noticed. (ii) XRD and Raman analyses show no peaks for the crystalline V2O5 phase, confirming the formation of a highly dispersed amorphous phase. For cerium, a crystalline CeO2 phase was confirmed in the 3.0 and 5.0 Ce-doped catalysts. (iii) TPR/TPO characterization displayed low- and hightemperature H2 reduction peaks for all the prepared catalysts, while the cyclic TPR/TPO and TGA showed a stable catalytic performance and thermal stability for the synthesized catalysts, respectively. (iv) The coexistence of both strong and weak acidic sites has been observed during NH3-TPD characterization. The NH3-TPD kinetics studies have shown a relatively weak metal−support interaction for the synthesized catalysts with activation energy of ammonia desorption following the subsequent trend: 5.0 Ce < 3.0 Ce < 1.0 Ce < 0.2 Ce < 0.0 Ce. (v) Among the synthesized catalysts, the 0.2 Ce catalyst showed a maximum selectivity of 62.4% (C4 olefin) at 450 °C and 5 s. Furthermore, the best catalytic performance was observed at low reaction temperatures and shorter residence times. (vi) The cerium-modified VOx/γ-Al2O3 displayed very low coke levels at 450 °C and 5 s reaction time, making it very adequate for its applications in continuous circulating fluidized bed operation. repeated TPR/TPO characterizations of the catalysts have also indicated the stable performance of the catalysts (see Table 3). Table 6 reports the comparison of the performance of the BODH catalyst of the current work with others reported in the Table 6. Comparison of BODH Catalyst Performance catalyst VOx/CeγAl2O3 VOx/MCM41 V2O5/MgOAl2O3 V2O5/MgOZrO2 VOx/USY VOx/USY Xa (%) Tb (°C) tc Sd (%) reactor system 10.7 450 5s 62.4 47.4 550 1h 57 fluidized bed fixed bed Wang et al.25 30.3 600 64.3 fixed bed Xu et al.12 32.9 500 6h 43.1 fixed bed Lee et al.74 5 520 4 56 fixed bed Garcia et al.27 68 fixed bed Volpe et al.22 Lemonidou et al.73 Rubio et al.75 Dejoz et al.76 min 8.2 520 4 min V2O5/MgO 29.5 520 54 fixed bed V2O5/MgO MoO3V2O5/ MgO 31.8 24.2 500 550 55.8 69.5 fixed bed fixed bed Article reference this work a X, n-butane conversion bT, reaction temperature ct, reaction time dS, selectivity of C4 olefins literature. The comparison is based on C4 olefin production. Wang et al. obtained 57% C4 olefin selectivity at 47.4% nbutane conversion at 550 °C using VOx/MCM-41 catalysts in a fixed-bed reactor.25 Similarly, Xu et al. have revealed 30.3% nbutane conversion with 64.3% C4 olefin selectivity using a 5%V2O5/MgO-Al2O3 catalyst at 600 °C in a fixed-bed reactor.12 In a separate study by Volpe et al., VOx as an active metal was impregnated on the surface of USY, α-Al2O3, NaY, and γ-Al2O3 catalyst supports. Among these catalysts, VOx/USY showed the best catalytic activity of 68% C4 alkene selectivity with a 8.2% n-butane conversion at 520 °C. In their analysis, gasphase O2-free conditions in a fixed-bed reactor were used.22 Furthermore, Garcia et al. also reported a VOx/USY catalyst at ■ AUTHOR INFORMATION Corresponding Author Mohammad M. Hossain − Department of Chemical Engineering and Center of Research Excellence in Nanotechnology, King Fahd University of Petroleum and 7419 https://dx.doi.org/10.1021/acs.energyfuels.0c00220 Energy Fuels 2020, 34, 7410−7421 Energy & Fuels pubs.acs.org/EF (15) Rischard, J.; Antinori, C.; Maier, L.; Deutschmann, O. Oxidative dehydrogenation of n-butane to butadiene with Mo-VMgO catalysts in a two-zone fluidized bed reactor. Appl. Catal. A Gen. 2016, 511, 23−30. (16) Owens, L.; Kung, H. H. The Effect of Loading of Vanadia on Silica in the Oxidation of Butane. J. Catal. 1993, 144, 202. (17) Wachs, I. E.; Weckhuysen, B. M. Structure and reactivity of surface vanadium oxide species on oxide supports. Appl. Catal. A Gen. 1997, 157, 67−90. (18) Chaar, M. A.; Patel, D.; Kung, M. C.; Kung, H. H. Selective oxidative dehydrogenation of butane over V-Mg-O catalysts. J. Catal. 1987, 105, 483−498. (19) Martin-Aranda, R. M.; Portela, M. F.; Madeira, L. M.; Freire, F.; Oliveira, M. Effect of alkali metal promoters on nickel molybdate catalysts and its relevance to the selective oxidation of butane. Appl. Catal. A, Gen. 1995, 127, 201−217. (20) Maldonado-Hódar, F. J.; Palma Madeira, L. M.; Farinha Portela, M. The Effects of Coke Deposition on NiMoO4Used in the Oxidative Dehydrogenation of Butane. J. Catal. 1996, 164, 399−410. (21) Blasco, T.; Nieto, J. M. L.; Dejoz, A.; Vazquez, M. I. Influence of the Acid-Base Character of Supported Vanadium Catalysts on Their Catalytic Properties for the Oxidative Dehydrogenation of nButane. J. Catal. 1995, 157, 271−282. (22) Volpe, M.; Tonetto, G.; de Lasa, H. Butane dehydrogenation on vanadium supported catalysts under oxygen free atmosphere. Appl. Catal. A Gen. 2004, 272, 69−78. (23) Bhattacharyya, D.; Bej, S. K.; Rao, M. S. Oxidative dehydrogenation of n-butane to butadiene. Appl. Catal. A Gen. 1992, 87, 29−43. (24) Wan, C.; Cheng, D.; Chen, F.; Zhan, X. Characterization and kinetic study of BiMoLax oxide catalysts for oxidative dehydrogenation of 1-butene to 1,3-butadiene. Chem. Eng. Sci. 2015, 135, 553− 558. (25) Wang, X.; Zhou, G.; Chen, Z.; Jiang, W.; Zhou, H. In-situ synthesis and characterization of V-MCM-41 for oxidative dehydrogenation of n-butane. Microporous Mesoporous Mater. 2016, 261−267. (26) Setnička, M.; Č ičmanec, P.; Bulánek, R.; Zukal, A.; Pastva, J. Hexagonal mesoporous titanosilicates as support for vanadium oxide Promising catalysts for the oxidative dehydrogenation of n-butane. Catal. Today 2013, 204, 132−139. (27) Garcia, E. M.; Sanchez, M. D.; Tonetto, G.; Volpe, M. A. Preparation of USY zeolite supported catalysts from V(AcAc)3 and NH4VO3. Catalytic eproperties for the dehydrogenation of n-butane in oxygen-free atmosphere. J. Colloid Interface Sci. 2005, 292, 179− 185. (28) Corrna, A.; Nieto, J. M. L.; Parades, N.; Dejoz, A.; Vazquez, I. Oxidative Dehydrogenation of Propane and N-Butane on V-Mg Based Catalysts. Stud. Surf. Sci. Catal. 1994, 82, 113−123. (29) Tanimu, G.; Jermy, B. R.; Asaoka, S.; Al-Khattaf, S. Composition effect of metal species in (Ni, Fe, Co)-Bi-O/gammaAl2O3 catalyst on oxidative dehydrogenation of n-butane to butadiene. J. Ind. Eng. Chem. 2017, 45, 111−120. (30) Rabindran Jermy, B.; Asaoka, S.; Al-Khattaf, S. Influence of calcination on performance of Bi−Ni−O/gamma-alumina catalyst for n-butane oxidative dehydrogenation to butadiene. Catal. Sci. Technol. 2015, 5, 4622−4635. (31) Jermy, B. R.; Ajayi, B. P.; Abussaud, B. A.; Asaoka, S.; AlKhattaf, S. Oxidative dehydrogenation of n-butane to butadiene over Bi−Ni−O/γ-alumina catalyst. J. Mol. Catal. A: Chem. 2015, 400, 121−131. (32) Solsona, B.; Concepción, P.; Hernández, S.; Demicol, B.; Nieto, J. M. L. Oxidative dehydrogenation of ethane over NiO−CeO2 mixed oxides catalysts. Catal. Today 2012, 180, 51−58. (33) Khan, M. Y.; Al-Ghamdi, S.; Razzak, S. A.; Hossain, M. M.; de Lasa, H. Fluidized bed oxidative dehydrogenation of ethane to ethylene over VOx/Ce-γAl2O3 catalysts: Reduction kinetics and catalyst activity. Mol. Catal. 2017, 443, 78−91. (34) Elbadawi, A. H.; Khan, M. Y.; Quddus, M. R.; Razzak, S. A.; Hossain, M. M. Kinetics of oxidative cracking of n-hexane to olefins Minerals, Dhahran 31261, Saudi Arabia; orcid.org/00000002-7780-5910; Phone: +966-13-860-1478; Email: mhossain@kfupm.edu.sa; Fax: +966-13-860-4234 Authors Muhammad Y. Khan − Department of Chemical Engineering, King Fahd University of Petroleum and Minerals, Dhahran 31261, Saudi Arabia Sagir Adamu − Department of Chemical Engineering, King Fahd University of Petroleum and Minerals, Dhahran 31261, Saudi Arabia Rahima A. Lucky − Department of Chemical and Biochemical Engineering, University of Western Ontario, London, Ontario N6A 3K7, Canada Shaikh A. Razzak − Department of Chemical Engineering, King Fahd University of Petroleum and Minerals, Dhahran 31261, Saudi Arabia Complete contact information is available at: https://pubs.acs.org/10.1021/acs.energyfuels.0c00220 Notes The authors declare no competing financial interest. ■ ACKNOWLEDGMENTS The author(s) would like to acknowledge the support provided by the Deanship of Scientific Research (DSR) at King Fahd University of Petroleum & Minerals (KFUPM) for funding this work through project no. IN161022. ■ Article REFERENCES (1) White, W. C. Butadiene production process overview. Chem.Biol. Interact. 2007, 166, 10−14. (2) Yan, W.; Kouk, Q. Y.; Luo, J.; Liu, Y.; Borgna, A. Catalytic oxidative dehydrogenation of 1-butene to 1,3-butadiene using CO2. Catal. Commun. 2014, 46, 208−212. (3) Grasselli, R. K. Fundamental principles of selective heterogeneous oxidation catalysis. Top. Catal. 2002, 21, 79−88. (4) Sattler, J. J. H. B.; Ruiz-Martinez, J.; Santillan-Jimenez, E.; Weckhuysen, B. M. Catalytic Dehydrogenation of Light Alkanes on Metals and Metal Oxides. Chem. Rev. 2014, 114, 10613−10653. (5) Bender, M. An Overview of Industrial Processes for the Production of Olefins - C4 Hydrocarbons. ChemBioEng Rev. 2014, 1, 136−147. (6) Madeira, L. M.; Portela, M. F. Catalytic oxidative dehydrogenation ofn-butane. Catal. Rev. 2002, 44, 247−286. (7) Fahim, M. A.; Alsahhaf, T. A.; Elkilani, A. Fundamentals of Petroleum Refining; Elsevier: 54, , 2010. (8) Al-Ghamdi, S. A.; de Lasa, H. I. Propylene production via propane oxidative dehydrogenation over VOx/γ-Al2O3 catalyst. Fuel 2014, 128, 120−140. (9) Kung, H. H. Oxidative Dehydrogenation of Light (C2 to C4) Alkanes. in Advances in Catalysis; 1994, volume 40, 1−38. (10) Cavani, F.; Trifirò, F. Partial oxidation of C2 to C4 paraffins. in Basic Principles in Applied Catalysis; 2004, 75, 19−84. (11) Blasco, T.; Nieto, J. M. L. Oxidative dyhydrogenation of short chain alkanes on supported vanadium oxide catalysts. Appl. Catal. A Gen. 1997, 157, 117−142. (12) Xu, B.; Zhu, X.; Cao, Z.; Yang, L.; Yang, W. Catalytic oxidative dehydrogenation of n-butane over V2O5/MO-Al2O3 (M = Mg, Ca, Sr, Ba) catalysts. Chinese J. Catal. 2015, 36, 1060−1067. (13) Vedrine, J. C. Heterogeneous catalytic partial oxidation of lower alkanes (C1−C6) on mixed metal oxides. J. Energy Chem. 2016, 25, 936−946. (14) Wang, C.; et al. Vanadium Oxide Supported on Titanosilicates for the Oxidative Dehydrogenation of n-Butane. Ind. Eng. Chem. Res. 2015, 54, 3602−3610. 7420 https://dx.doi.org/10.1021/acs.energyfuels.0c00220 Energy Fuels 2020, 34, 7410−7421 Energy & Fuels pubs.acs.org/EF over VOx/Ce-Al2O3 under gas phase oxygen-free environment. AIChE J. 2017, 63, 130−138. (35) Shang, X.; et al. Facile strategy for synthesis of mesoporous crystalline γ-alumina by partially hydrolyzing aluminum nitrate solution. J. Mater. Chem. 2012, 22, 23806. (36) Wang, J.; Shang, K.; Guo, Y.; Li, W.-C. Easy hydrothermal synthesis of external mesoporous γ-Al2O3 nanorods as excellent supports for Au nanoparticles in CO oxidation. Microporous Mesoporous Mater. 2013, 181, 141−145. (37) Adamu, S.; Khan, M. Y.; Razzak, S. A.; Hossain, M. M. Ceriastabilized meso-Al2O3: synthesis, characterization and desorption kinetics. J. Porous Mater. 2017, 24, 1343−1352. (38) Elbadawi, A. H.; Khan, M. Y.; Quddus, M. R.; Razzak, S. A.; Hossain, M. M. Kinetics of oxidative cracking of n-hexane to olefins over VOx /Ce-Al2O3under gas phase oxygen-free environment. AIChE J. 2017, 63, 130−138. (39) De Lasa, H. I. Canadian Patent 1,284,017,(1991). USA Pat 5, (1992). (40) Sedor, K. E.; Hossain, M. M.; de Lasa, H. I. Reactivity and stability of Ni/Al2O3 oxygen carrier for chemical-looping combustion (CLC). Chem. Eng. Sci. 2008, 63, 2994−3007. (41) Do, D. D. Adsorption Analysis: Equilibria and Kinetics. Chemical Engineering; 2, (Imperial College Press: 1998). (42) Bortolozzi, J. P.; Weiss, T.; Gutierrez, L. B.; Ulla, M. A. Comparison of Ni and Ni−Ce/Al2O3 catalysts in granulated and structured forms: Their possible use in the oxidative dehydrogenation of ethane reaction. Chem. Eng. J. 2014, 246, 343−352. (43) Sun, Q.; et al. Studies on the improved thermal stability for doped ordered mesoporous γ-alumina. Phys. Chem. Chem. Phys. 2013, 15, 5670. (44) Khodakov, A.; Yang, J.; Su, S.; Iglesia, E.; Bell, A. Structure and properties of vanadium oxide-zirconia catalysts for propane oxidative dehydrogenation. J. Catal. 1998, 177, 343−351. (45) Bakare, I. A.; et al. Fluidized bed ODH of ethane to ethylene over VOx−MoOx/γ-Al2O3 catalyst: Desorption kinetics and catalytic activity. Chem. Eng. J. 2015, 278, 207−216. (46) Trovarelli, A. Catalytic Properties of Ceria and CeO 2 -Containing Materials. Catal. Rev. 1996, 38, 439−520. (47) Reddy, E. P.; Varma, R. S. Preparation, characterization, and activity of Al2O3-supported V2O5 catalysts. J. Catal. 2004, 221, 93− 101. (48) Martinezhuerta, M.; et al. Oxidative dehydrogenation of ethane to ethylene over alumina-supported vanadium oxide catalysts: Relationship between molecular structures and chemical reactivity. Catal. Today 2006, 118, 279−287. (49) Kašpar, J.; Fornasiero, P.; Graziani, M. Use of CeO2-based oxides in the three-way catalysis. Catal. Today 1999, 50, 285−298. (50) Koranne, M. M.; Goodwin, J. G.; Marcelin, G. Characterization of Silica- and Alumina-Supported Vanadia Catalysts Using Temperature Programmed Reduction. J. Catal. 1994, 148, 369−377. (51) Nakajima, Y.; et al. Ingestion of Hijiki seaweed and risk of arsenic poisoning. Appl. Organomet. Chem. 2006, 20, 557−564. (52) Sasikala, R.; Gupta, N. M.; Kulshreshtha, S. K. Temperatureprogrammed reduction and CO oxidation studies over Ce-Sn mixed oxides. Catal. Letters 2001, 71, 69−73. (53) Yao, H. Ceria in automotive exhaust catalysts I Oxygen storage. J. Catal. 1984, 86, 254−265. (54) Bartholomew, C. H. Fundamentals of industrial toxicology. Food and Chemical Toxicology; 20, (1982). (55) Cvetanović, R. J.; Amenomiya, Y. Application of a Temperature-Programmed Desorption Technique to Catalyst Studies. in Adv. Catal. 1967, 17, 103−149. (56) Topsoe, N. Infrared and temperature-programmed desorption study of the acidic properties of ZSM-5-type zeolites. J. Catal. 1981, 70, 41−52. (57) Chen, W.-H.; et al. A solid-state NMR, FT-IR and TPD study on acid properties of sulfated and metal-promoted zirconia: Influence of promoter and sulfation treatment. Catal. Today 2006, 116, 111− 120. Article (58) Yan, W.; et al. Improving oxidative dehydrogenation of 1butene to 1,3-butadiene on Al2O3 by Fe2O3 using CO2 as soft oxidant. Appl. Catal. A Gen. 2015, 508, 61−67. (59) Datka, J.; Turek, A. M.; Jehng, J. M.; Wachs, I. E. Acidic properties of supported niobium oxide catalysts: An infrared spectroscopy investigation. J. Catal. 1992, 135, 186−199. (60) Wu, Z.; Jin, R.; Liu, Y.; Wang, H. Ceria modified MnOx/TiO2 as a superior catalyst for NO reduction with NH3 at low-temperature. Catal. Commun. 2008, 9, 2217−2220. (61) Lee, K. J.; et al. Ceria added Sb-V2O5/TiO2 catalysts for low temperature NH3 SCR: Physico-chemical properties and catalytic activity. Appl. Catal. B Environ. 2013, 142-143, 705−717. (62) Cvetanović, R. J.; Amenomiya, Y. A Temperature Programmed Desorption Technique for Investigation of Practical Catalysts. Catal. Rev. 1972, 6, 21−48. (63) Tonetto, G.; Atias, J.; De Lasa, H. FCC catalysts with different zeolite crystallite sizes: Acidity, structural properties and reactivity. Appl. Catal. A Gen. 2004, 270, 9−25. (64) Al-Ghamdi, S.; Volpe, M.; Hossain, M. M.; De Lasa, H. VOx/cAl2O3 catalyst for oxidative dehydrogenation of ethane to ethylene: Desorption kinetics and catalytic activity. Appl. Catal. A Gen. 2013, 450, 120−130. (65) Hossain, M. M.; de Lasa, H. I. Reactivity and stability of CoNi/Al2O3 oxygen carrier in multicycle CLC. AIChE J. 2007, 53, 1817−1829. (66) Owen, O. S.; Kung, M. C.; Kung, H. H. The effect of oxide structure and cation reduction potential of vanadates on the selective oxidative dehydrogenation of butane and propane. Catal. Letters 1992, 12, 45−50. (67) Boullosa-Eiras, S.; Vanhaecke, E.; Zhao, T.; Chen, D.; Holmen, A. Raman spectroscopy and X-ray diffraction study of the phase transformation of ZrO2−Al2O3 and CeO2−Al2O3 nanocomposites. Catal. Today 2011, 166, 10−17. (68) Francisco, M. S. P.; Mastelaro, V. R.; Nascente, P. A. P.; Florentino, A. O. Activity and Characterization by XPS, HR-TEM, Raman Spectroscopy, and BET Surface Area of CuO/CeO2 -TiO2 Catalysts. J. Phys. Chem. B 2001, 105, 10515−10522. (69) Patel, D.; Andersen, P. J. Oxidative Dehydrogenation of Butane over Orthovanadates. J. Catal. 1990, 125, 132−142. (70) Armendariz, H.; et al. Oxidative dehydrogenation of n-butane on zinc-chromium ferrite catalysts. J. Mol. Catal. 1994, 92, 325−332. (71) Soler, J.; López Nieto, J. M.; Herguido, J.; Menéndez, M.; Santamaría, J. Oxidative Dehydrogenation ofn-Butane in a Two-Zone Fluidized-Bed Reactor. Ind. Eng. Chem. Res. 1999, 38, 90−97. (72) Cavani, F.; Ballarini, N.; Cericola, A. Oxidative dehydrogenation of ethane and propane: How far from commercial implementation? Catal. Today 2007, 127, 113−131. (73) Lemonidou, A.; Tjatjopoulos, G.; Vasalos, I. Investigations on the oxidative dehydrogenation of n-butane over VMgO-type catalysts. Catal. Today 1998, 45, 65−71. (74) Lee, J. K.; et al. Oxidative dehydrogenation of n-butane over Mg3(VO4)2/MgO−ZrO2 catalysts: Effect of oxygen capacity and acidity of the catalysts. J. Ind. Eng. Chem. 2012, 18, 1758−1763. (75) Rubio, O.; Herguido, J.; Menéndez, M.; Grasa, G.; Abanades, J. C. Oxidative dehydrogenation of butane in an interconnected fluidized-bed reactor. AIChE J. 2004, 50, 1510−1522. (76) Dejoz, A.; López Nieto, J. M.; Márquez, F.; Vázquez, M. I. The role of molybdenum in Mo-doped V−Mg−O catalysts during the oxidative dehydrogenation of n-butane. Appl. Catal. A Gen. 1999, 180, 83−94. 7421 https://dx.doi.org/10.1021/acs.energyfuels.0c00220 Energy Fuels 2020, 34, 7410−7421