Promotional Effect of Manganese on Selective Catalytic Reduction of NO by CO in the Presence of Excess O 2 over M@La – Fe/AC (M = Mn, Ce) Catalyst

: The catalytic performance of a series of La-Fe/AC catalysts was studied for the selective catalytic reduction (SCR) of NO by CO. With the increase in La content, the Fe 2+ /Fe 3+ ratio and amount of surface oxygen vacancies (SOV) in the catalysts increased; thus the catalytic activity improved. Incorporating the promoters to La3-Fe1/active carbon (AC) catalyst could affect the catalyst activity by changing the electronic structure. The increase in Fe 2+ /Fe 3+ ratio after the promoter addition is possibly due to the extra synergistic interaction of M (Mn and Ce) and Fe through the redox equilibrium of M 3+ + Fe 3+ ↔ M 4+ + Fe 2+ . This phenomenon could have improved the redox cycle, enhanced the SOV formation, facilitated NO decomposition, and accelerated the CO-SCR process. The presence of O 2 enhanced the formation of the C(O) complex and improved the activation of the metal site. Mn@La3-Fe1/AC catalyst revealed an excellent NO conversion of 93.8% at 400 °C in the presence of 10% oxygen. The high catalytic performance of MnO x and double exchange behavior of Mn 3+ and Mn 4+ can increase the number of SOV and improve the catalytic redox properties.


Introduction
Nitrogen oxide (NOx) is mainly emitted from stationary and mobile combustion processes and causes many problems such as global warming, ozone depletion, photochemical smog, acid rain, visibility damage, and human health complications. Many efforts have recently been devoted to reduce and control NOx from the air using different technologies, such as selective catalytic reduction (SCR) that converts harmful NOx to harmless N2. Considerable attention has been given to the development of SCR of NOx using CO, which can efficiently remove NO and CO co-existing in many industrial exhaust gases [1][2][3]. However, this method has several challenges, such as resistance to O2 and SO2, ensuring low-temperature activation, and durable operation. The CO-SCR process shows great potential for expanded application because CO is low cost and can be simply produced without generating solid carbon deposits [4,5].
provide the highest catalytic activity. The influence of catalyst composition on the physicochemical properties and catalyst activity for the CO-SCR reaction was investigated in the presence of 10% oxygen. The promotional effect of manganese and cerium on the catalyst properties and NOx conversion was studied. The prepared catalysts were characterized by Raman spectroscopy, X-ray diffraction (XRD), temperature-programmed desorption (CO-TPD and NO-TPD), inductively coupled plasma-optical emission spectrometry (ICP-OES), and X-ray photoelectron spectroscopy (XPS).

Characterization of Catalysts
The molecular vibration or rotational energy and the structural disorder degree of the synthesized catalysts were studied using Raman spectroscopy. This technique is used widely for characterizing structural features of carbon materials. Figure 1, Table S1, and Figure S1 revealed that all La-Fe/AC catalysts had two peaks. A distinct peak appeared at approximately 1340 cm −1 (D band) assigned to the chaos and defects of the crystalline structure of carbon material, and the peak appeared at around 1600 cm −1 (G bands) assigned to the graphitic structure of carbon materials [33,34]. The value of ID/IG was used to evaluate the degree of graphitization level, reflecting the structural proximity degree of carbon material. The lower ID/IG ratio designates a well-ordered structure of the carbon material in the catalysts. The ID/IG values of catalysts were in the following order: Mn@La3-Fe1/AC (2.03) > Ce@La3-Fe1/AC (1.70) > La3-Fe1/AC (1.63) > La1-Fe1/AC (1.51) > La1-Fe3/AC (1.42) > Fe/AC (0.98) > AC (0.94). There was an increase in the ID/IG ratio after loading Fe and La on AC support and reached 1.63 for the La3-Fe1/AC catalyst, indicating the formation of more graphitized carbon at a higher concentration of La in the catalyst structure. A further increase was observed after the addition of promoters, and the highest ID/IG was observed for the Mn@La3-Fe1/AC catalyst. This result implies that the addition of promoters increased the extent of graphitization. The Mn@La3-Fe1/AC with the larger ID/IG value indicated that the catalyst's crystalline structure was slightly ruined during the preparation process compared with other catalysts.
The XRD spectra of different catalysts are shown in Figure 2. The main component of rawactivated carbon is carbon, having the main peaks with numerous clutter peaks. Two diffraction peaks attributed to AC were detected at 26° (002) and 43° (101) (JCPDS card No 41-1487). The peaks of Fe were observed in Fe/AC catalyst. The peaks at around 35° (311) and 50° (511) were assigned to Fe3O4 (JCDS card No. 04-0755), and peaks at around 44.5°, 58°, and 64° were attributed to Fe2O3 [17,21,[34][35][36]. The intensities of the diffraction peaks of Fe3O4 and Fe2O3 were decreased by the addition of La, Mn, and Ce, and the peaks became wider, indicating the better metal dispersion on the catalysts. Weak peaks at around 28.4°, 39.5°, and 53° were assigned to the presence of La2O3 in the catalysts (JCPDS card No. 05-0602). As shown in Figure 2, the intensities of the peaks for metal oxides were very weak, and also some of them were overlapped with the broad and intense carbon peaks, and the crystalline structure of iron oxides and lanthanum oxide were not clearly detected. Intensity of the peaks are proportional to the amount of the materials detected by X-ray. Due to the low amount of loaded materials in the catalyst, high dispersion, or poor crystalline state of promoter atoms, the intensity of the peaks were very weak or not observed. There are very weak peaks of Mn and Ce in XRD patterns. The weak peak corresponds to Mn3O4 was observed at around 18.6° in the XRD pattern of Mn@La3-Fe1/AC, and CeO2 peaks were observed at 33.8° (200) and 56.5° (311) (JCPDS card No. 34-0394) in the XRD pattern of Ce@La3-Fe1/AC [1,4,17]. The first small peak at around 13.7° could belong to the plastic sample holder because the irradiated area of the sample was 15 × 15 mm, but the investigated powders were located only in the area of 12 × 12 mm. The XPS technique was used to analyze the composition and surface properties of La-Fe/AC. The surface elemental composition and oxidation state of the catalysts were analyzed using XPS in the region of 0-1300 eV. The XPS survey spectrum and surface composition of the synthesized catalysts ( Figure 3 and Table 1) indicated that the prepared catalysts contained Fe, La, C, O, Mn, and Ce elements. La:Fe ratios obtained from the XPS analysis were not very close to the nominal composition of the prepared catalysts. The reason could be that the XPS is highly surface selective and will reflect the composition at the surface and only a few nanometers deep down, which could be different from the elemental composition in the bulk sample. The chemical compositions of the prepared catalysts were also analyzed by inductively coupled plasma-optical emission spectrometry (ICP-OES) ( Table 1). It was found that La:Fe ratios of the prepared catalysts were close to the nominal molar ratios of La and Fe for all samples.   Figure 4 shows the XPS spectra of Fe 2p assigned to different catalysts. The observed peaks at 711.2 and 725.5 eV were attributed to the binding energies of Fe 2p3/2 and Fe 2p1/2, respectively. The values of 709 and 711 eV were reported for Fe 2+ (2p3/2) and Fe 3+ (2p3/2), respectively [17,35,37]. The shake-up satellite peaks at 714.02, 718.57, 731.67, and 734.40 eV correspond to Fe 2p3/2 and Fe 2p1/2 [19]. The peak at around 711.2 eV was assigned to the Fe 2p3/2 peaks of iron oxides, confirming that both ferrous and ferric oxides were present. Increasing the amount of La in the catalyst structure increased the ratio of Fe 2+ /Fe 3+ ( Table 1). The presence of both Fe 2+ and Fe 3+ was also confirmed by XRD analysis; however, due to the overlapping of the peaks for metal oxides with the wide and intense peaks of carbon materials, the crystalline structure of iron oxides were not clearly identified.

Binding Energy (eV)
The formation of Fe 2+ might be attributable to the higher electronegativity of Fe (1.83) compared with La (1.10); therefore, Fe's tendency to capture electrons is higher than that of La. Hence, compared with La 3+ , Fe 3+ can easily accept the electrons to form more Fe 2+ and resulted in a higher Fe 2+ /Fe 3+ ratio and improved catalytic activity [38]. The redox couple (Fe 2+ /Fe 3+ ) in Fe/AC catalyst indicated an electron transfer between Fe and AC supports. The catalyst activity could be affected by the incorporation of promoters, which act as a structural modifier and alter the surface properties by affecting the metal-support interaction, thus improving the metal dispersion and number of active metals and enhancing the catalyst reducibility.
XPS analysis of the catalyst (Table 1) revealed that the Fe 2+ /Fe 3+ ratio increased by adding Ce and Mn promoters to the catalyst. Further increase in the Fe 2+ after addition of promoter could be due to the new synergistic interaction of M (Mn or Ce) and Fe through the redox equilibrium of M 3+ + Fe 3+ ↔ M 4+ + Fe 2+ . The redox couples between Fe 2+ /Fe 3+ and M 3+ /M 4+ could improve the redox cycle, enhance the oxygen vacancies, facilitate the NO dissociation, and promote the catalytic reaction. According to the results, the amount of Fe 2+ species on the surface of Mn@La3-Fe1/AC catalyst was higher than other catalysts (Fe 2+ /Fe 3+ = 1.96), which resulted in enhanced catalytic activity in NO reduction by CO at low temperature. Figure 5 and Table 2 display the XPS spectra and curve fittings of O 1s used to investigate the oxygen species on the catalysts' surface. The O 1s spectra of Fe/AC catalyst showed three different peaks. The first peak centered at 530.5 eV, ascribed to the lattice oxygen (Oβ) with low binding energy related to metal-oxide (Fe-O) bond. The second peak at 531.6 eV could be ascribed to O 2− ions in the oxygen-deficient regions, representing the surface chemisorbed oxygen (Oα) in the matrix of catalysts. The peak at 532.9 eV could be assigned to the oxygen species in hydroxide groups and dissociated   Incorporation of Ce and Mn to the La3-Fe1/AC catalyst resulted in a further increase in the number of oxygen vacancies on the catalysts' surface and improved the catalytic activity. Incorporation of Mn increased the number of surface chemisorbed oxygen (Oα) and lattice oxygen (Oβ). The surface chemisorbed oxygen with high mobility is the most active oxygen species in the SCR process. The oxygen in the gas phase can be activated by the surface chemical oxygen on the catalyst's surface, it can facilitate the oxidation of NO to NO2 and thus accelerating the CO-SCR process [16,[44][45][46]. Chang et al. [20] studied the surface properties of LaFeO3 perovskite catalysts. They reported that the peak with the lowest binding energy between 527 and 531 eV was attributed to the lattice O species, whereas the chemisorbed O or OH − or hydroxides species, and particularly adsorbed water species were observed at the highest binding energies between 530 and 536 eV. As shown in Figure 5, the Oα was found to be the main peak of O 1s for Mn@La3-Fe1/AC catalyst. As it has been reported other researchers [16,47], the catalytic reaction of NO and CO could be enhanced at higher amount of Oα, which could be due to the fact that in addition to oxidizing of CO, the Oα also promote the adsorption of NO on the active sites of the catalyst. Evaluation of catalytic activity of binary Fe-Co metal oxides on semi-coke for the NO + CO reaction also revealed that the catalyst with the higher amount of Oα exhibited the highest deNOx activity [16]. It has been proposed that this high activity was attributed to the higher amount of Brønsted acid sites, high possibility of formation oxygen vacancies, and the strong redox performance. Yao et al. [47] also reported that the catalyst with the higher surface oxygen vacancies revealed the higher activity and oxygen vacancies play an important role in NO removal by CO reaction.

Binding Energy (eV)
The surface oxygen species is a critical factor for the NO reduction by CO, which can oxidize CO and promote the NO adsorption. The higher amount of Oα indicating the presence of more active oxygen on the surface of the catalyst. The higher oxygen vacancies, together with the higher Fe 2+ /Fe 3+ ratio, resulted in the better catalytic performance by facilitating NO dissociation. The interaction between different species in metal oxide catalysts plays an essential role in the reduction of NO by CO. As mentioned earlier, due to the higher electronegativity of Fe, the electrons can migrate to Fe 3+ to generate more Fe 2+ in the catalyst, so the solid-state charge transfer redox couple on mixed-oxide catalysts (M 3+ + Fe 3+ ↔ M 4+ + Fe 2+ ) could promote the catalytic performance. The redox cycle could shift to right through varying La:Fe ratio, as well as the addition of promoters, which consequently could enhance the catalytic activity.
A critical factor for the NO reduction by CO is the catalyst ability of NO adsorption/desorption. The NO-TPD results are shown in Figure 6a. NO desorption peaks were observed at around 100-250 °C and 350-600 °C, indicating that NO was adsorbed on different active sites. The desorption peaks at lower temperatures indicating the bridge nitrates on the catalyst, and these low-temperature peaks attributed to the desorption of physically adsorbed NO from the catalysts' surface. The peaks at higher temperatures (350-600 °C) indicating the presence of a large number of NOx species (nitrates and nitrites), with high thermostability on the surface, which could be decomposed at high temperatures [9,48,49].
NO molecules were activated by the SOVs to produce N and O radicals. The O radicals were reacting with adsorbed CO molecules on Fe 2+ species to produce CO2, and N radicals could be combined with another NO molecule to make N2O or combined with another N radical to produce N2. N2O can be considered as the intermediate for NO reduction into N2. These findings are in good accordance with the results reported by Shi et al. [19], who studied the Mn-modified copper and iron catalysts and investigated their catalytic activity for NO reduction by CO. It was found that the Mn 4+ on the surface of the catalyst can generate reactive oxygen species, which can be more easily reduced to create some oxygen vacancies during the reaction. The CO-TPD analysis was performed to study the CO adsorption behavior on the catalyst's surface ( Figure 6b). As shown in CO-TPD profiles, two peaks appeared at around 350-550 °C and 600-750 °C, indicating the presence of different types of activated adsorption sites with different binding strengths on the surface of the catalysts. CO was difficult to desorb from Fe/AC at low temperatures. The lanthanum addition to the catalyst affected the CO desorption behavior, and desorption peaks shifted to lower temperatures. According to the areas under the CO-TPD graphs, the amount of desorbed CO from the surface of the catalyst increased by the addition of La to Fe/AC. The peaks were growing and shifting to the lower temperatures by adding Ce and Mn into the catalyst; thus, the CO adsorption capacity increased. It is believed that the Fe 2+ species on the catalyst's surface are the active sites for CO adsorption. The higher temperature of adsorption and desorption of CO for Fe/AC catalyst, together with a lower amount of Fe 2+ , can result in the low catalytic activity in NO reduction by CO. Presence of the desorption peaks at lower temperatures for the promoted catalysts attributed to the rich Fe 2+ species on the catalyst's surface, which was also confirmed by the XPS analysis (Table 1). According to the areas under the CO-TPD graphs, the total amount of desorbed gas is following the order: Mn@La3-Fe1/AC (1809) > Ce@La3-Fe1/AC (1612) > La1-Fe3/AC (1014) > La3-Fe1/AC (577) > La1-Fe1/AC (385) > Fa/AC (338). Among these catalysts, the Mn@La3-Fe1/AC exhibited the lowest desorption temperature, which could be ascribed to the higher content of Fe 2+ on the catalyst surface, resulting in the slightly higher catalytic activity in the NO + CO reaction.

Catalytic Activity Evaluation
The catalytic activity can be influenced by catalyst nature and its structure, such as uniform dispersion of metal species, high surface area, and mesoporous structure. Figure 7a shows that the maximum NO conversion of 64.4% was obtained for Fe/AC at 400 °C. The addition of transition metal oxides into the catalyst can improve the redox properties and thermal stability of the composite materials. It has been reported that the carbon-based materials loaded with transition metals reveal high activity in NOx reduction by CO [16,50]. The physicochemical properties of the catalyst can affect the catalytic pathway [51,52]. The addition of La can be beneficial for NO conversion into N2 and further enhancement of the catalytic activity [53,54]. The lanthanum with the electronic structure of 4f 0 5d 1 6s 2 has only one electron in 5d orbital and can provide proper electron transfer orbital. The rare earth elements compounds have high catalytic activity and can be used as catalysts for the electron transfer station [55]. Increasing the amount of La enhanced the NO conversion at the temperature range between 200-400 °C. Figure 7a shows that the La3-Fe1/AC catalyst with a higher content of La showed the highest NOx conversion compared with other catalysts. As it was mentioned earlier, the characterization results revealed that the variation of La:Fe ratio in the catalysts resulted in different interactions between La and Fe, which affects the formation of Fe 2+ and Fe 3+ species, whereas the Fe 2+ /Fe 3+ ratio increased from 0.58 for La1-Fe3/AC to 0.81 for La3-Fe1/AC. The higher Fe 2+ /Fe 3+ ratio enhanced the CO adsorption and NO dissociation and resulted in higher catalytic activity. The large gradient of electronegativity between La (1.10) and Fe (1.83) is useful for shifting the redox equilibrium to the right and generating more Fe 2+ species on the surface of the catalyst. During the catalyst preparation via the co-impregnation method, the low-valence-state Fe species and additional oxygen vacancies were created, enhancing the adsorption of CO and dissociation of NO species and improve the catalytic activity. The obtained results for the catalyst activity tests were in good consistent with the XPS and TPD results. The activity test revealed that the Mn@La3-Fe1/AC catalyst with the highest Fe 2+ /Fe 3+ ratio (obtained from XPS analysis) has the highest activity. NO reduction by CO was enhanced by the synergistic effect of SOV and Fe 2+ species.
In the absence of oxygen and 400 °C, the NOx conversions of 77.3%, 79.4%, and 88.4% for La1-Fe3/AC, La1-Fe1/AC, and La3-Fe1/AC were obtained, respectively (Figure 7a). Ramana et al. [27] found that the changes in the surface chemical composition and structural properties of La2O3 led to improved catalytic activity and stability of the catalysts. Lanthanum nitrate (La[NO3]3) was converted to La2O3 after calcination and improved the NOx conversion.
In the presence of 10% O2 at 400 °C, the NOx conversion increased slightly to 60.3%, 81.4%, 84.7%, and 89.7% for Fe/AC, La1-Fe3/AC, La1-Fe1/AC, and La3-Fe1/AC, respectively (Figure 7b). The O2 was adsorbed into the carbon site of the support to form C(O) complex. The reaction of C(O) with an oxidized metal site (*O) that formed CO2 and activated the metal site (*) can be used later for the reduction of NO to N2O or N2. The mechanism can be expressed as the following reactions [56]: 2NO + C→N2 + CO2 (8) C(NO) + *NO ↔ CO + *N2O (10) According to this reaction mechanism, the presence of the metal site is crucial for the gasification of carbon and the reaction of NO and carbon sites. The presence of O2 in the flue gas can enhance the creation of a C(O) complex and improve the activation of the metal site (*). O2 can significantly affect the NO reduction by carbon because of the enhancement effect of surface oxygen complex. More than 80% of NO conversion was obtained at 400 °C in the presence of 10% O2. The roles of carbon sites, oxygen, and metal sites in the NO reduction are exhibited in reactions 1, 2, 3, 9, and 10.
It is worth mentioning that a negligible amount of NO2 (less than 5 ppm) was detected for all catalysts in the presence of oxygen during the reaction. Actually, by the addition of oxygen to the feed gas, about 10-50 ppm NO2 was formed due to the fast homogeneous gas-phase oxidation of NO to NO2 (NO + O2 → 2 NO2); and after about 2 min of reaction, NO2 concentration was significantly decreased to less than 5 ppm, remained almost constant till the end of the reaction. Then, the formed NO2 reacted with CO and produce N2 (2 NO2 + 4 CO → N2 + 4 CO2) [57]. The NO2 formation during the reaction in the absence of oxygen was also negligible during 6 h of reaction (less than 5 ppm). The NOx conversion of 90.4% was achieved at 400 °C for the Ce@La3-Fe1/AC catalyst (Figure 8a). The addition of Ce as a promoter to the catalyst can enhance the low-temperature activity of the catalyst and the ability for NOx reduction and also increase the catalyst stability [58,59]. Oxygen can be absorbed by Ce in reductive conditions and released in oxidative conditions for oxidation because of reversible conversion between electronic states Ce 3+ and Ce 4+ . It has been reported that the incorporation of Ce 4+ into the lattice of La 3+ resulted in the formation of solid solution and increased the catalyst resistance against sintering at high temperatures, which stabilized the active metals [60]. The maximum NOx conversion of 92.7% was obtained for Mn@La3-Fe1/AC catalyst in the absence of oxygen at 400 °C because of the high catalytic performance of MnOx (Figure 8a). In comparison with other metals, manganese (Mn) is a less toxic component that can be used as a catalyst for the SCR of NO [61]. Chen et al. [17] reported that the modification of Fe2O3/AC catalysts with Mn species resulted in a high dispersion of manganese and iron oxides over the AC support, a larger surface area, higher amounts of Mn 4+ /Mn 3+ , and stronger reduction ability, which caused an enhancement in the SCR performance of the catalyst. The presence of O2 resulted in a slight enhancement in the NOx conversion of the catalyst by increasing the surface oxygen complex. Thus, Figure 8b shows the NOx conversion of Ce@La3-Fe1/AC and Mn@La3-Fe1/AC enhanced to 91.8% and 93.8%, respectively, in the presence of 10% O2. Figures 7 and 8 show that the NOx conversion over the La-Fe/AC catalyst was enhanced by increasing the temperature from 200 °C to 400 °C. The elevation of the temperature could result in increasing the SOV formation. Increasing the reaction temperature can provide adequate energy for dissociation of NO on SOV. Additionally, Fe 2+ can adsorb the CO molecules during CO oxidation, thereby resulting in an improved reaction. The chemisorption of CO on active metal sites and increased SOV on the catalyst's surface resulted in the enhanced catalytic performance in the CO-SCR reaction.

Catalyst Preparation
A commercial activated carbon (Sigma-Aldrich, Prague, Czech Republic) was used as a support material. The AC was pretreated by soaking in the acid mixture of HNO3 and H2SO4 (HNO3:H2SO4 ratio of 3:1 [v/v]) for 24 h at room temperature with gentle shaking. The samples were then filtered and washed with deionized water. Then, the AC was dried at 110 °C for 24 h. The catalysts supported on AC with different molar ratios of La:Fe (i.e., 0:1, 1:1, 1:0, 1:3, and 3:1) with the total metal loading of 20 wt.% were prepared using the co-impregnation method. The proper amounts of precursors of Fe(NO3)3·9·H2O (99.999%, Sigma-Aldrich, Prague, Czech Republic) and La(NO3)3·6·H2O (98%, Sigma-Aldrich, Prague, Czech Republic) were dissolved in deionized water and added dropwise to the AC support with constant stirring for 6 h. The obtained impregnates then dried at 120 °C for 12 h followed

Catalyst Characterization
The X-ray diffractometer with Cu Kα radiation (k = 1.5408 Å) at 60 kV and 80 mA (XRD, D8 ADVANCE Rigaku D/max-RB, Tokyo, Japan) was used to study the phase structure of the catalysts. The Raman analysis for the samples was performed using DXR Raman Microscopy, using backscattering geometry with a Nd:YVO4 DPSS (532 nm) laser source. The spectra were recorded in the range of 500-2500 cm −1 with a spectral resolution of 1 cm −1 . X-ray photoelectron spectroscopy (XPS) spectra of the samples were obtained using the Thermo Scientific K-alpha photoelectron spectrometer (Waltham, MA, USA). The Thermo Scientific™ Avantage Software was used for XPS data processing. Inductively coupled plasma-optical emission spectrometer (ICP-OES, Agilent 725, Agilent Technologies Inc., Santa Clara, CA, USA) was used to determine the catalysts' composition, after the total digestion of the sample in aqua regia. The temperature program desorption (TPD) of NO and CO analysis were performed through a flow reactor equipped with a thermal conductivity detector (TCD). The requisite amount of catalyst was heated from room temperature to 300 °C (10 °C/min), held for 60 min in helium flow of 30 mL/min, and then cooled down to room temperature. The sample was then exposed to 5 vol.% NO/He for NO-TPD and 10 vol.% CO/He for CO-TPD for 30 min. Afterward, helium was purged for 30 min to eliminate the physically adsorbed CO and NO from the surface of the sample. The sample was then heated to 600 °C (CO-TPD) and 800 °C (NO-TPD) in helium flow with a rate of 10 °C/min. The TCD was used to monitor the consumption of NO and CO during the analysis. Mettler Toledo thermal analysis system was used to measure weight changes of the sample when heated under a flow of nitrogen and also air at a constant heating rate of 10 °C/min from 25 °C to 900 °C.

Catalyst Activity Test
The catalyst activity was measured in a fixed-bed tubular reactor at atmospheric pressure using 400 mg of catalyst powder at a temperature range between 200 °C to 400 °C. Figure 9 shows the schematic of the experimental setup. The stainless steel K-Type thermocouple temperature sensor was located inside the reactor tube, near the catalyst bed. The catalyst was flushed in-situ with helium at 200 °C for 1 h before the activity measurement. The furnace temperature was adjusted to the required reaction temperature, and the reactor was supplied with the reactant gas mixture with a composition of 250 ppm NO, 0%-10% O2, and 5000 ppm CO in He. The total flow rate of the feed gas was 350 mL/min with the gas hourly space velocity (GHSV) of 26,000 h −1 . The concentration of NO and CO in feed gas was determined according to the industrial flue gas, which contains 100-1000 ppm NO and 2000-50,000 ppm CO, respectively. The composition of the outlet gas (including NO, NO2, NOx) during 6 h of reaction was analyzed using a chemiluminescence analyzer (CAI-600 HCLD, California Analytical Instruments, CA, USA). The NOx conversion was calculated using the following equation: where , is the initial concentration of NOx, and , is the concentration of NOx in the outlet gas. Figure 9. Schematic of the fixed-bed tubular reactor for the CO-SCR reaction.

Conclusions
The reduction of NOx by CO offers a simple and low-cost technology for reducing NOx emissions from mobile or stationary sources. In this study, NOx removal by CO was investigated over a series of La-Fe catalysts supported on activated carbon synthesized using co-impregnation. Based on the above experiments, the paper mainly draws the following conclusions: La-containing catalysts showed enhanced NO conversion compared to Fe/AC catalyst. Introducing La into the catalysts increased the Fe 2+ /Fe 3+ ratio, and SOV in the catalysts, thereby improving the catalytic activity. Incorporation of Ce and Mn also increased the number of oxygen vacancies and lattice oxygen and facilitated the oxidation of NO to NO2, and so accelerated the CO-SCR process. The synergistic interaction of promoter agent (Mn and Ce) and Fe through the redox equilibrium of M 3+ + Fe 3+ ↔ M 4+ + Fe 2+ resulted in a further increase in the amount of Fe 2+ . The redox couples may have improved the redox cycle and consequently enhanced the formation of oxygen vacancies, facilitated NO decomposition, and promoted the catalytic reaction. The Mn-modified catalyst with better dispersion of the amorphous state, high amounts of Fe 2+ /Fe 3+ and Mn 4+ /Mn 3+ , and SOV amount showed the highest catalytic activity. The increased number of SOV can improve the catalyst's redox properties because of the double exchange behavior of Mn 3+ and Mn 4+ . The NOx conversion of 92.7% was obtained over Mn@La3-Fe1/AC catalyst in the absence of oxygen at 400 °C; this catalyst also exhibited NOx conversion of 93.8% in the presence of 10% oxygen and at 400 °C.
In future work, the effects of reductive pretreatments and different promoters' concentrations on the performance of catalysts will be investigated. Additional analyses to find the most available oxygen atoms and the maximum reducibility of the catalysts could be beneficial for evaluating the physicochemical properties of the catalysts.

Supplementary Materials:
The following are available online at www.mdpi.com/2073-4344/10/11/1322/s1, Figure S1: Raman spectroscopy of the prepared catalysts, Figure S2: XPS spectrum of La3d, Ce3d and Mn2p of the La-Fe/AC catalysts, Figure S3: TGA analysis for AC, under air and nitrogen, Table S1: Raman Spectroscopy analysis for the prepare catalysts, Table S2: Details for the peak deconvolution XPS spectrum of the prepared catalysts.
Author Contributions: Conceptualization and experimental work designed and supported by F.G. and Z.G.; the characterizations, catalyst evaluation, and analysis were done by F.G., Z.G., M.T., V.V., S.M. and M.V.; the manuscript was written and amended by F.G. and Z.G. All authors have read and agreed to the published version of the manuscript.
Funding: This publication is a result of the project CATAMARAN, Reg. No. CZ.02.1.01/0.0/0.0/16_013/0001801, which has been co-financed by European Union from the European Regional Development Fund through the Operational Programme Research, Development and Education. This project has also been financially supported by the Ministry of Industry and Trade of the Czech Republic which has been providing institutional support for long-term conceptual development of research organisation. The project CATAMARAN has been integrated into the National Sustainability Programme I of the Ministry of Education, Youth and Sports of the Czech Republic (MEYS) through the project Development of the UniCRE Centre (LO1606). The result was achieved using the infrastructure of the project Efficient Use of Energy Resources Using Catalytic Processes (LM2018119) which has been financially supported by MEYS within the targeted support of large infrastructures. The result was also developed within the CENTEM project, reg. no. CZ.1.05/2.1.00/03.0088, cofunded by the ERDF as part of the Ministry of Education, Youth and Sports OP RDI programme and, in the follow-up sustainability stage, supported through CENTEM PLUS (LO1402) by financial means from the Ministry of Education, Youth and Sports under the "National Sustainability Programme I".