3.1. Influence of various preparation methods
Figure 1 depicts the X-ray diffraction (XRD) patterns of the 20NiO-Al2O3 samples synthesized employing diverse methods. The discerned diffraction peaks located at 2θ = 37.6°, 45.2°, 63.7°, and 66.3° were linked to the existence of nickel aluminate (JCPDS 10–0339)[44]. The X-ray diffraction (XRD) patterns demonstrated distinct peaks at 2θ = 43.4° and 76.4°, which can be ascribed to the existence of the NiO phase (JCPD 04-0850)[45]. At 2θ = 37.6°, 63.7°, and 66.3°, the diffraction peaks of the NiAl2O4 have overlapped with Al2O3 diffraction peaks (code N. 73-1519) [45].
The outcomes suggested that the utilization of the sol-gel metod resulted in the formation of the 20NiO-Al2O3 catalyst exhibiting the most significant crystallite size when compared to the other catalysts synthesized. Regarding the sample synthesis employing the sol-gel technique, the X-ray diffraction analysis unveiled distinct peaks aligning with the NiO phase at 43.4° and 76.4°. However, notably absent were any discernible diffraction peaks corresponding to nickel aluminate, as observed at 45.2° and 63.7°. Due to the low intensity of the peaks in the sample synthesized by mechanochemical and impregnation methods, the NiO dispersion on the catalyst surface was found to be higher in these samples compared to the others.
Figure 2a depicts the adsorption/desorption isotherms, while Fig. 2b exhibits the pore size distributions of the 20NiO-Al2O3 catalysts synthesized employing varied preparation methods. The isotherm shapes observed for the 20NiO-Al2O3 catalysts, excluding the specimen synthesized through the combustion technique, can be categorized as type IV isotherms with an H2-type hysteresis loop. This indicates the presence of a mesoporous structure with cylindrical-shaped pores in these materials.
The results unveiled that the sample synthesized through the combustion method displayed an isotherm of type II, accompanied by an H3-type hysteresis loop. This indicates the existence of a mesoporous and macroporous structure characterized by non-uniform sizes or shapes within the catalyst. The pore size distributions of all catalysts, except for the combustion catalyst, were observed to fall within the 2–20 nm range, as illustrated in Fig. 2b. The 20NiO-Al2O3 catalyst prepared by the combustion method has a much larger pore size than the sample synthesized with the mechanochemical method [46–48].
Table 2 provides the textural characteristics of the NiO-Al2O3 catalysts synthesized utilizing various methods. The results indicated that the sample synthesized via the co-precipitation technique displayed the highest specific surface area (241.5 m2.g− 1), whereas the sample prepared via the combustion method demonstrated the lowest specific surface area (49.4 m2.g− 1). Nevertheless, comparable trends were noted in relation to the pore volume of the samples prepared through different methods.
Table 2
Textural properties of the 20NiO-Al2O3 catalysts prepared by different preparation methods
Catalyst
|
Specific surface area (m2/g)
|
Pore volume
(cm3/g)
|
Pore size
(nm)
|
Average crystallite size
(nm)
|
Mechanochemical
|
240.7
|
0.32
|
5.28
|
29.4
|
Sol-gel
|
138.5
|
0.17
|
4.95
|
53.8
|
Combustion
|
49.4
|
0.10
|
12.37
|
38.2
|
Impregnation
|
205.7
|
0.28
|
2.97
|
33.5
|
Co-precipitation
|
241.5
|
0.32
|
2.53
|
36.8
|
The Scherrer equation was utilized for the computation of the crystallite size of nickel oxide. The calculations showed that the sample synthesized through the sol-gel method had the largest crystallite size (53.8 nm) among all the investigated catalysts. This result is consistent with the XRD findings previously discussed. Based on the obtained results, it was observed that the sample synthesized using the mechanochemical method exhibited the smallest crystallite size. This implies that the mechanochemical method resulted in better dispersion of NiO on the catalyst surface compared to the other preparation methods.
The reducibility characteristics of the calcined 20NiO-Al2O3 catalysts, prepared using diverse methods, were assessed using temperature-programmed reduction (TPR) analysis. The TPR curves acquired for the catalysts are illustrated in Fig. 3. The obtained results demonstrated that the various preparation methods have various reduction behaviors. The TPR analysis disclosed that the 20NiO-Al2O3 catalysts displayed a reduction peak occurring in the temperature range of 600–1000°C. This peak corresponds to the reduction of NiO, signifying a notable interaction between NiO and the alumina support. Additionally, the reduction of the formed NiAl2O4 phase in the catalyst was also observed during the TPR analysis.
The results showed that the samples synthesized with combustion and co-precipitation methods had less reduction intensity among the prepared samples. Furthermore, it was noted that the specimen synthesized through the sol-gel method displayed the most pronounced reduction peak. The highest temperature of this reduction peak was also elevated in comparison to the other samples. This behavior can be ascribed to the higher content of NiAl2O4 species, which requires higher temperatures for reduction. Additionally, it was noticed that the reduction peak of the sample synthesized via the impregnation method shifted towards lower temperatures. This shift suggests a weaker interaction between the metal and the support.
The catalytic performance of the 20NiO-Al2O3 catalysts synthesized through different methods was evaluated in the carbon dioxide methanation process. Figure 4a and 4b illustrate the conversion of CO2 and selectivity of CH4 for the diverse catalysts under investigation. The results indicated that the sol-gel and mechanochemical synthesis methods resulted in the 20NiO-Al2O3 catalysts exhibiting higher carbon dioxide conversion rates at lower temperatures.The higher CO2 conversion can be linked to improved reducibility and higher concentration of active species exhibited by the catalysts synthesized using these methods. Also, the catalyst synthesized by the impregnation method showed the lowest CO2 conversion during the reaction. The results of methane selectivity also showed the high methane selectivity for the catalysts synthesized by combustion, mechanochemical, and sol-gel methods.
At a temperature of 400°C, the 20NiO-Al2O3 catalyst prepared through the mechanochemical method, possessing a specific surface area of 240.7 m2/g, exhibited carbon dioxide conversion rate of 68.17% with a methane selectivity of 96.06%. This was while the highest carbon dioxide conversion (79.19%) at 450°C belonged to the 20NiO-Al2O3 catalyst synthesized using the co-precipitation method.
Overall, the results highlight that the catalyst synthesized using the mechanochemical method showcased the most elevated CO2 conversion rates and CH4 selectivity, particularly at lower temperatures. Consequently, the mechanochemically NiO(20)-Al2O3 was selected in this section, and the influence of the various nickel loading was studied over this catalyst.
3.2. NiO(X)-Al2O3 catalysts
Figure 5 presents the X-ray diffraction (XRD) patterns of the NiO-Al2O3 catalysts featuring diverse nickel loadings spanning from 5 to 25 wt.%. The X-ray diffraction (XRD) profiles of the NiO- Al2O3 catalysts revealed the emergence of the NiO phase peak at 37.4°, and the diffraction peaks of Al2O3 and NiAl2O4 appeared at 37.4°, 46.2° and 66.8° (JCPDS 10–0339), respectively [44].
The XRD pattern depicted in Fig. 5 unveils the distinct diffraction peaks, signifying the coexistence of multiple overlapping species. The results exhibited an augmentation in the intensity of the diffraction peaks situated at 2θ = 37.4°, 46.2°, and 66.8° as the nickel content increased. The diffraction peaks associated with the Al2O3 and NiAl2O4 phases were appeared at the angle of 19.8° by increasing the nickel contents. The acquired results indicated that an increase in the intensity of the diffraction peaks linked to nickel oxide cuased by the elevation in nickel content. Furthermore, the larger particles formed in the catalyst possessing a higher nickel content.
Due to the similar lattice parameters between gamma-alumina and nickel aluminate, it is difficult to distinguish between the diffraction peaks of Al2O3 and the NiAl2O4 phase. This overlap in the diffraction patterns could be attributed to the pseudo spinel structure of gamma-alumina, further complicating the identification of these phases. When the percentage of nickel was increased increased, resulting in an excess amount of alumina in the Ni-Al2O3 catalyst, this led to a heightened presence of particles in contact with alumina. This increased contact between nickel and alumina promoted the formation of the NiAl2O4 spinel phase [49, 50].
Figures 6a and 6b showcase the nitrogen adsorption/desorption isotherms and pore size distributions of the NiO-Al2O3 catalysts, each characterized by distinct nickel loadings. Based on the analysis of the isotherms shown in Fig. 6a, the isotherm classifications can be attributed to type IV, a characteristic indicative of materials possessing a mesoporous structure with cylindrical-shaped pores.
The presence of an H2-type hysteresis loop within the isotherms signifies the presence of mesopores within the structure of the synthesized samples. This specific arrangement of the H2 hysteresis loop is often associated with spherical solids composed of interconnected particles featuring varying sizes and shapes, resulting in the formation of edge pores. The presence of the hysteresis loop at low P/P0 values in all the catalysts indicates the formation of small pores.
The detection of an H2-shaped hysteresis loop at elevated partial pressures within the sample possessing higher nickel loadings implies an augmentation in the pore size of the catalyst. However, largest pore size was obtained for the catalyst containing 15 wt. % of Ni. According to the data presented in Fig. 6b, the pore size distribution profiles ranged from 2 to 9 nm and shifted towards higher values with increasing Ni loadings.
Table 3 outlines the textural characteristics of the NiO-Al2O3 catalysts with differing nickel loadings. As the nickel loading increased, there was a reduction in pore volume from 0.38 to 0.31 cm3/g and a decline in specific surface area from 268.8 to 235.6 m2/g. This can be attributed to the combination of NiO powder, which possesses a low specific surface area, with alumina, which exhibits a high specific BET area. The interaction between these constituents results in a notable decrease in the specific surface area. The pore size of the samples exhibited a rise with the increment in nickel loading, reaching its maximum at 15 wt%. However, further increases in nickel loading led to a reduction in pore size. This observation is consistent with the findings presented in Fig. 6b.
Table 3
Textural properties of NiO-Al2O3 catalysts with various nickel loadings
Catalyst
|
Specific surface area (m2/g)
|
Pore volume
(cm3/g)
|
Pore size
(nm)
|
Average crystallite size
(nm)
|
5NiO-Al2O3
|
268.8
|
0.38
|
5.49
|
11.0
|
10NiO-Al2O3
|
257.3
|
0.36
|
5.63
|
13.9
|
15NiO-Al2O3
|
249.2
|
0.34
|
5.78
|
20.9
|
20NiO-Al2O3
|
240.7
|
0.32
|
5.28
|
29.4
|
25NiO-Al2O3
|
235.6
|
0.31
|
5.21
|
30.8
|
The application of the Scherrer equation allowed the calculation of nickel oxide crystallite size. The findings indicated that augmenting the nickel content from 5 to 25 wt. % within the catalyst structure resulted in an escalation of the average NiO crystallite size, ranging from 11.0 to 30.8 nm. This suggests a reduction in the dispersion of nickel oxide within the catalyst.
The results obtained from the temperature-programmed reduction (TPR) analysis carried out on the NiO-Al2O3 catalysts featuring different nickel loadings are presented in Fig. 7. The observed reduction peak in the TPR analysis corresponds to the reduction of highly interactive NiO species with alumina, as well as the reduction of the NiAl2O4 spinel phase. The limited reduction characteristics have resulted in the absence of reduction peaks for the catalysts containing 5 and 10 wt. % of NiO. With the increase of nickel loadings from 15 to 25 wt. %, the reduction peak was detected within the temperature range of 660–1000°C. This indicates the reduction of NiO species that exhibit strong interactions with alumina and the reduction of the NiAl2O4 spinel phase [16].
The creation of NiAl2O4 spinel during the calcination process is primarily attributed to the potent interaction between nickel species and alumina at high temperatures. This strong interaction promotes the creation of the spinel phase in the catalyst. By elevating the nickel loading in the catalyst, it was noted that the highest temperature (Tmax) of the main reduction peak was detected at lower temperatures. This shift indicates a weaker interaction between Al2O3 and Ni in the catalyst. The enhanced nickel loading led to an increase in the size of the nickel crystallites. The reduction peak area and intensity decreased as the percentage of nickel decreased due to the lower concentration of nickel and reduced H2 consumption. Samples featuring a low nickel percentage displayed diminished reducibility at high temperatures, primarily attributed to the formation of NiAl2O4 [50, 51].
The comparison of the catalytic performance among the NiO-Al2O3 catalysts with NiO contents spanning from 5 to 25 wt. % is presented in Fig. 8. The equilibrium conversion has been obtained through simulating the equilibrium reaction of CO2 methanayion in HYSYS software.
As depicted in Fig. 8a, the catalysts performance exhibited enhancement with the augmentation of nickel loading, reaching its peak efficiency at 20 wt.%. This can be attributed to enhanced reducibility and the increased concentration of active species within the catalysts as the nickel content rises. Nevertheless, a reduction in the conversion rate was discerned upon elevating the NiO loading to 25 wt. %. This can be explained by the negative influence of the high concentration of active metal on the dispersion of nickel and the lower BET surface area observed in this particular catalyst. A decrease in nickel loading is recognized to diminish the count of active sites, leading to a reduction in catalyst activity. It is important to highlight that the number of active sites is closely linked to the dispersion of nickel particles on the surface of the catalyst. With a rise in nickel content, the active site count decreases, thereby leading to a reduction in the dispersion of nickel throughout the catalyst. At a specific nickel loading, the catalyst manifests its peak activity, stability, and selectivity.
According to Fig. 8b, the NiO (20)-Al2O3 catalyst showed the best performance for methane selectivity. For catalysts with 20 and 25 wt. % Ni loading, the carbon dioxide conversion showed improvement up to 450°C. However, at higher reaction temperatures, both the conversion of CO2 and selectivity of CH4 exhibited a decrease. This can be ascribed to the concurrent operation of the reverse water-gas shift reaction alongside the primary reaction [38, 52, 53]. The 20NiO-Al2O3 catalyst showed 71.47% conversion of carbon dioxide along with 94.82% methane selectivity at 450 ℃. The 20wt%Ni-Al2O3 catalysts results showed 48% CO2 conversion and 5wt.% Ni/Al2O3 showed 1.8% CO2 conversion at 350°C with GHSV = 16000 h− 1 and H2/CO2 = 4. The 20wt%Ni-Al2O3 catalysts showed 48% CO2 conversion at 350°C with GHSV = 56.7 h-1 and H2/CO2/N2 = 60:15:20 ml/min.
3.3. Temperature of calcination:
Figure 9 displays the XRD patterns of the 20NiO-Al2O3 catalysts synthesized through mechanochemical method and calcined at various temperatures. Elevating the calcination temperature promoted the generation of NiAl2O4 and led to heightened crystallinity within the prepared samples. As the calcination temperature was raised, the intensity of the peaks related to the NiO, Al2O3, and NiAl2O4 phases was intensified. This can be linked to the higher crystallite size of the catalysts and a reduction in the dispersion of nickel particles on the catalyst surface.
As the calcination temperature is elevated, the data in Table 4 demonstrates an augmentation in the crystallite size alongside a reduction in the BET surface area. These alterations can be ascribed to the sintering process experienced by particles at higher calcination temperatures. The collapse of the pore structure increased by raising the calcination temperature. This can be associated with dominant impact of the calcination temperature, which alters the catalyst's structure. Furthermore, raising the calcination temperature led to an increase in pore size. This can be attributed to the destruction and collapse of small mesopores at higher calcination temperatures.
Table 4
Textural properties of the mechanochemically 20NiO-Al2O3 catalyst calcined at different temperatures
Catalyst
|
Specific surface area (m2/g)
|
Pore volume
(cm3/g)
|
Pore size
(nm)
|
Average crystallite size
(nm)
|
Calcined at 400 ̊C
|
276.3
|
0.36
|
5.28
|
26.9
|
Calcined at 500 ̊C
|
240.7
|
0.32
|
5.25
|
29.4
|
Calcined at 600 ̊C
|
205.1
|
0.38
|
7.33
|
32.4
|
Figure 10a portrays the N2 adsorption/desorption isotherms of the 20NiO-Al2O3 catalysts subjected to various calcination temperatures. Figure 10b presents the corresponding pore size distribution profiles. The physisorption isotherms depicted in Fig. 10a can be categorized as type IV, along with an H2-type hysteresis loop. The results demonstrated that as the calcination temperature increased, the hysteresis loop emerged at higher partial pressures, implying a rise in pore size. The profiles of pore size distribution for the 20NiO-Al2O3 catalysts after calcination at varying temperatures, as shown in Fig. 10b, exhibited a range of pore sizes from 2 to 20 nm. The results revealed that with the increase of the calcination temperature, the distribution of pore sizes shifted towards larger magnitudes, signifying an increase in the proportion of larger pores within the catalysts.
Figure 11 illustrates the TPR profiles of the 20NiO-Al2O3 catalysts that have undergone different calcination temperatures. All samples exhibited one broad reduction peak between 600 to 1000°C, indicating the reduction of nickel oxide with a strong interaction with alumina and the generation of nickel aluminate. Nevertheless, the results demonstrated that with the increase of the calcination temperature, the reduction peak shifted towards higher temperatures. This shift can be ascribed to the increased formation of nickel aluminate spinel and a stronger interaction between nickel and alumina. For the catalyst calcined at a temperature of 400°C, the Tmax value was approximately 800°C, suggesting the reduction of NiO accompanied by an interaction with the alumina support. The peak intensity became more pronounced as the calcination temperature increased. The catalyst with a calcination temperature of 600°C exhibited a peak at approximately 900°C, attributable to the reduction of NiAl2O4, an inactive phase in the methanation reaction.
Figure 12 presents the results of FESEM analysis, which was carried out to investigate the impact of the calcination temperature on the morphology of the prepared catalysts. According to the obtained results, it can be deduced that raising the calcination temperature led to particle aggregation, with the catalyst calcined at 600°C displaying the largest particles and the lowest specific surface are
Figures 13a and 13b illustrate the outcomes of CO2 conversion and CH4 selectivity, respectively, for the 20NiO-Al2O3 catalysts subjected to different calcination temperatures. The results exhibited a reduction in the efficiency of the calcined 20NiO-Al2O3 catalyst in the CO2 methanation process as the calcination temperature was incresed. This suggested that the interaction between the different phases of the 20NiO-Al2O3 catalyst was altered with the elevation of calcination temperature. Raising the calcination temperature resulted in a decrease in the quantity of accessible active sites and the specific surface area of the catalyst. Based on the findings, the 20NiO-Al2O3 catalyst subjected to calcination at 400°C showcased the most superior performance. The 20NiO-Al2O3 catalyst calcined at 400°C showed 80.68% carbon dioxide conversion along with 98.3% methane selectivity at 400°C.
3.4. Effect of operating conditions:
Figure 14 depicts the influence of Gas Hourly Space Velocity (GHSV) on the performance of the 20NiO-Al2O3 catalyst during the CO2 methanation process at a temperature of 350°C. The results demonstrated a decline in CO2 conversion and CH4 selectivity as the GHSV value increased.This can be ascribed to the increased flow rate of the inlet feed to the reactor, resulting in reduced adsorption time of carbon dioxide and shortened reaction time between carbon dioxide and hydrogen on the catalyst surface [13, 18]. The highest performance was achieved at a GHSV value of 9000 ml/h.gcat, resulting in a carbon dioxide conversion of 54.24% and methane selectivity of 97.87%.
Figure 15 depicts the impact of the H2/CO2 molar ratio on the carbon dioxide conversion and the methane selectivity at an operational temperature of 350°C. The carbon dioxide conversion increased from 37.74–52.35% and the methane selectivity increased from 89.89–94.42% as the H2/CO2 ratio was increased from 3 to 4.5. The enhancement observed in the performance of the 20NiO-Al2O3 catalyst, achieved through an elevation in the H2/CO2 molar ratio, can be attributed to the heightened presence of hydrogen available for the reaction with carbon dioxide. This increase in availability facilitates an augmented interaction between CO2 and H2 on the catalyst surface, a phenomenon that has been elucidated in previous research [52].
The exploration of the impact of temperature at which reduction occurs on the effectiveness of the 20NiO-Al2O3 catalyst encompassed the alteration of temperatures within the range of 400 to 600°C. The corresponding outcomes are presented in Fig. 16a and 16b. The efficiency of the 20NiO-Al2O3 catalyst within the CO2 methanation process demonstrated an upward trend in efficiency corresponding to increasing reduction temperature. Under the operational temperature of 400°C, a substantial rise in carbon dioxide conversion was observed, elevating from 7.6–82.55%, accompanied by a remarkable augmentation in methane selectivity, ranging from 18.37–97.87%. This improvement in performance stemmed from the heightened availability of active sites capable of adsorbing carbon dioxide. At 400 ℃, the incomplete reduction of the catalyst led to a reduced concentration of active sites located on the surface of the catalyst, thereby contributing to suboptimal catalytic performance.
Figure 17 depicts the thermal stability of the 20NiO-Al2O3 catalyst in the process of carbon dioxide methanation at 350°C for 12h. The 20NiO-Al2O3 catalyst exhibited remarkable stability, as the CO2 conversion and CH4 selectivity remained nearly constant throughout the reaction period. The alteration in morphology between the fresh and spent 20NiO-Al2O3 catalysts was evaluated through FESEM analysis, and the corresponding results are depicted in Fig. 17b and 17c. No indications of carbon deposition on the catalyst surface were observed following the stability test. Furthermore, it is noteworthy to mention that an augmentation in particle size was noted after the stability test, which can be attributed to thermal sintering and enhanced particle agglomeration at elevated temperatures.
The CO Methanation reaction was carried out using the 20NiO-Al2O3 catalyst, and a comparison between CO and CO2 methanation is presented in Fig. 18. The activity of the surface active sites on the 20NiO-Al2O3 catalyst varied between the CO and CO2 methanation processes. The 20NiO-Al2O3 catalyst demonstrated higher performance in the CO Methanation process compared to the CO2 methanation process. The selectivity of methane in the CO Methanation process remained nearly constant and reached 100%. The RWGS reaction was not performed under this condition in CO Methanation. At a temperature of 450°C, the conversion of CO to methane reached 98.16%, while the conversion of CO2 to methane at the same temperature reached 71.24%. The higher carbon monoxide conversion (CO) compared to carbon dioxide (CO2) can be attributed to the stronger interactions between CO and the catalyst surface. The findings suggested that the existence of nickel on the catalyst surface might obstruct specific adsorption sites for carbon dioxide (CO2), leading to a lowered catalytic activity for the CO2 methanation process [54–56].