Biogas dry reforming over Ni/LnOx-type catalysts (Ln = La, Ce, Sm or Pr)
Introduction
The Glasgow Pact, resulting from COP26, expressed alarm at the fact that around 1.1 °C of warming has been caused by human activities, and at the rapid depletion of the Earth's remaining carbon budget consistent with 1.5 °C. Worryingly, despite the efforts undertaken over the past few decades to develop renewable energy resources, fossil fuels still provide around 80% of the world's energy supply [1,2]. Our reliance on fossil-based energy, apart from threatening the survival of our species, is also responsible for more immediate concerns related to the accessibility and affordability of these resources (and ultimately equity), especially since the continuity of supply is subject to the political will of only a handful of countries, which are often undemocratic or disregard the rule-based international order, as so vividly made clear by the recent events unfolding in Eastern Europe.
The use of biomass, as well as the utilization of CO2, have long been identified as key pillars on which the future energy and chemical industry can be based [[3], [4], [5], [6], [7]]. Biogas in particular, a product of the anaerobic digestion of organic wastes, not only constitutes a promising renewable energy resource, but it can simultaneously provide an efficient way to manage the ever-increasing amounts of municipal, industrial and agricultural wastes [8,9]. Although the composition of biogas depends heavily on the type of biomass from which its being produced, it mainly consists of CH4 (50–75%) and CO2 (25–45%), i.e., the main greenhouse gases, water vapor (2–8%) and trace amounts of O2, N2, NH3, H2, H2S [9,10], siloxanes, chlorides, and volatile organic compounds [11]. Biogas has a lower energy density than natural gas, which hinders application in combustion engines, however, its high CO2 content makes it an ideal candidate for dry reforming applications (Eq. (1)) [[11], [12], [13], [14]].
The dry reforming of biogas, in essence the dry reforming of methane (DRM), (Eq. (1)), is highly endothermic and produces syngas with a theoretical 1:1 H2:CO molar ratio [15,16]. However, the process also poses the formidable challenge of controlling catalyst deactivation due to coke deposition, and the sintering of the metallic particles (e.g., Ni), that constitute the active phase. The former is induced mainly via the decomposition of CH4 (Eq. (2)) and the disproportionation of CO (Boudouard reaction) (Eq. (3)) [17,18]. The latter is the result of the high temperature required to overcome the Gibbs free energy barrier of the reverse Boudouard reaction (700 °C) and the reverse water gas shift (RWGS) reaction (815 °C) (Eq. (4)) [19,20].
The product of the DRM reaction, syngas, a mixture of CO and H2, can be converted via Fischer-Tropsch synthesis to a wide range of hydrocarbons [21] or via the water gas shift (WGS) reaction to H2. Although the interest in hydrogen energy has waxed and waned over the past few decades, technological advancements in its scaled-up production and storage mean that the sector is in the cusp of a much-anticipated boom [22,23]. Hydrogen has numerous advantages in comparison to other energy carriers, as its combustion does not emit CO2 or CO and can be used for both electricity production and transportation [23,24]. At present, 98% of H2 is being produced using naphtha, methane and coal [25], which means that efforts to produce it in a sustainable way should be intensified.
Thus, it is urgent to develop catalytic systems with increased activity and durability at relatively low reaction temperatures. Although noble metals materials, such as Rh, Pt, Pd, and Ru have been shown to be highly active and more resistant to carbon deposition [26], Ni-based catalysts have attracted considerable research interest, as they too show good activity but are also much cheaper in comparison, advantages that make them an attractive choice for potential industrial applications. However, Ni-based catalysts present two major drawbacks, as they are prone to, firstly, the formation of coke on their surface (which covers the active sites and blocks the porous system), and secondly, to the aggregation of Ni nanoparticles (a result of the high reaction temperatures), a phenomenon that reduces the population of active sites on the catalysts surface [[27], [28], [29]]. As shown by a number of works in the literature [30,31], coke deposition can be minimized by supporting materials with oxygen vacancies, increased oxygen storage capacity, and surface basic sites, while smaller Ni nanoparticles in enhanced interaction with the support can restrict the agglomeration of Ni nanoparticles.
A plethora of metal oxides (e.g., Al2O3, ZrO2, CeO2, La2O3) and multi-composite oxides have been widely used as supporting materials in reforming reactions of biogas [12,32]. Dan et al. [33] investigating the catalytic performance of Ni/γ-Al2O3 and Ni/CeO2/γ-Al2O3 catalysts (concentrations of Ce equal to 5 and 15 wt%) in the reaction of steam reforming of biogas argued that ceria-containing catalysts presented the highest CH4 and CO2 conversion values for the entire temperature range, due to the larger dimension of pores, the better reducibility, the improved intimate contact between Ni, alumina and cerium oxide, and the more stable Ni nanoparticles. Armbruster et al. [34], studying the effects of promoters (Gd, Sc, La) on the stability of Ni-based catalyst during biogas dry reforming, argued that the addition of Sc and of Gd caused the generation of stronger metal-support interaction (SMSI) reinforcing the stabilization of Ni nanoparticles during the reaction, which is very important to prevent catalyst deactivation. It has also been shown that La2O3, due to its basic characteristics, favors the adsorption and dissociation the gaseous CO2, reinforcing the catalytic activity at relatively low temperature range [29,35]. Furthermore, the presence on La2O3 on the catalyst surface enhances the resistance of the catalyst against deactivation due to the formation of La2O2CO3, which reinforces the removal of coke deposits from adjacent Ni nanoparticles [29,35].
To avoid sintering and coke formation, the idea of stabilizing active metals as ionic lattice sites in stable structured perovskite oxides has attracted considerable research attention. Perovskites can be described by the general formula ABO3, where A can be an alkali or alkaline earth, or rare earth metal (e.g., La, Sr, Ca, Ce, Pr, Sm) and B can be a transition metal (e.g., Ni, Co, Fe, Mn) [36]. The catalytic activity of these materials depends on the nature of A and B elements, synthesis method used and their partial substitution. They have controllable structure, high thermal stability and high catalytic efficiency, which makes them ideal candidates for processes carried out at high temperatures, like biogas dry reforming [37]. Usually, in the DRM and other methane conversion reactions, the perovskite-derived catalysts are more active and stable compared to supported catalytic materials, due to the stronger metal-oxide interaction and the higher dispersion of the active sites [37,38]. In the case of Ni-based perovskites, gradual reduction of Ni occurs to form highly dispersed Ni nanoparticles with high activity and resistance to coke formation under DRM conditions, which is sometimes accompanied by the destruction of the initial perovskite matrix (e.g., in the case of LaNiO3) [37]. Additionally, different methods have been proposed in the literature (i.e., Pechini [39], sol-gel [40], co-precipitation [41], auto-combustion [42]) to synthesize perovskites with increased surface area and small crystallite sizes.
The experimental research study presented herein investigates the structure, physicochemical properties, and catalytic performance of Ni/LnOx (Ln = La, Ce, Sm, Pr) catalytic materials in synthesis gas production from biogas via the dry reforming process. The samples were prepared via the citrate sol-gel method and thoroughly characterized. The investigation of the catalytic activity was carried out in the temperature range of 600–750 °C, while short and long time-on-stream experiments were performed under different reaction conditions in order to investigate coke deposition and the degree of aggregation of the Ni active sites.
Section snippets
Catalyst synthesis
The calcined catalyst precursors of NiO-LnOx type (Ln = La, Ce, Sm, Pr, referred to as LNO, CNO, SNO and PNO, respectively) were synthesized by employing the citrate sol-gel method [43]. The initial step was the dissolution of appropriate amounts of metal nitrates (i.e., Ni(NO3)2·6H2O and La(NO3)3·6H2O, Ce(NO3)3·6H2O, Pr(NO3)3·6H2O or Sm(NO3)3·6H2O, depending on the sample) in 100 mL of deionized water. Citric acid was then added to the solution. The molar ratio of Ni to Ln was 1:1 and that of
Crystallinity
X-ray diffraction patterns of the calcined (NiO-LnOx; note that Ln stands for Lanthanide) and reduced (Ni/LnOx) materials are presented in Fig. 1a and b, respectively. Regarding the calcined LNO sample, the typical diffractogram of phase pure orthorhombic LaNiO3 is observed [46,47]. However, for the other calcined systems the perovskite structure could not be formed (Fig. 1a), despite the high calcination temperature applied (900 °C). In particular, the CNO sample presents diffraction peaks,
Conclusions
This work reported on the synthesis of NiO-LnOx mixed oxides (Ln = La, Ce, Sm or Pr, equimolar ratio of Ni and Ln) via a citrate sol-gel synthesis method. In the case of La, close to phase-pure LaNiO3 perovskite crystallites were formed, due to the favorable thermodynamics for perovskite-phase formation. On the other hand, the use of the other lanthanides led to the formation of segregated NiO-LnOx oxides. Catalyst reduction led to the formation of metallic Ni nanoparticles, which were
Declaration of competing interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgments
The authors gratefully acknowledge the Ministry of Science and Technology (MOST) of the People's Republic of China providing funds through the National Key Research and Development Program (project code:2017YFE013330). The authors also gratefully acknowledge that this research has been co-financed by the European Union and Greek national funds under the call “Greece – China Call for Proposals for Joint RT&D Projects” (Project code: T7DKI-00388). V.S. acknowledges the assistance of the
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