Abstract
Direct conversion of biogas via the integrative process of dry reforming of methane (DRM) and catalytic methane decomposition (CDM) has received a great attention as a promising green catalytic process for simultaneous production of syngas and carbon nanotubes (CNTs). In this work, the effects of reaction temperature of 700–1100 °C and CH4/CO2 ratio of biogas were investigated over NiMo/MgO catalyst in a fixed bed reactor under industrial feed condition of pure biogas. The reaction at 700 °C showed a rapid catalyst deactivation within 3 h due to the formation of amorphous carbon on catalyst surface. At higher temperature of 800–900 °C, the catalyst can perform the excellent performance for producing syngas and carbon nanotubes. Interestingly, the smallest diameter and the highest graphitization of CNTs was obtained at high temperature of 1000 °C, while elevating temperature to 1100 °C leads to agglomeration of Ni particles, resulting in a larger size of CNTs. The reaction temperature exhibits optimum at 800 °C, providing the highest CNTs yield with high graphitization, high syngas purity up to 90.04% with H2/CO ratio of 1.1, and high biogas conversion (XCH4 = 86.44%, XCO2 = 95.62%) with stable performance over 3 h. The typical composition biogas (CH4/CO2 = 1.5) is favorable for the integration process, while the CO2 rich biogas caused a larger grain size of catalyst and a formation of molybdenum oxide nanorods (MoO3). The long-term stability of NiMo/MgO catalyst at 800 °C showed a stable trend (> 20 h). The experimental findings confirm that NiMo/MgO can perform the excellent activity and high stability at the optimum condition, allowing the process to be more promising for practical applications.
Similar content being viewed by others
Explore related subjects
Find the latest articles, discoveries, and news in related topics.Introduction
The rapid increase in greenhouse gases (GHGs) paves global warming as one of the most concerning global issues. Dry reforming of methane (DRM), as one of the three alternative methane reactions for methane reforming, has been considered as an efficient solution for contributing to the depletion of the two main components of greenhouse gases (CO2 and CH4) through converting it into synthesis gas (the mixture of H2 and CO) (Eq. (1)) compared with other two cases (Eqs. (2) and (3))1,2,3,4,5,6,7,8,9. Dry reforming of methane (DRM) is a particularly attractive process owing to this process avoids the expensive and intricate gas separation process separation costs results in the overall operation cost to produce high purity syngas being estimated to be 20% lower10. It provides a potential pathway for using biogas due to its high content of CH4 and CO2. Biogas is considered a renewable and sustainable energy strategy11 produced via anaerobic digestion or fermentation of any biodegradable organic matter, including municipal solid waste, sewage sludge, agricultural wastes, animal dung, and energy crops of organic waste materials12. According to the world biogas production from 2000 to 2014, biogas increased by 357% to 59 billion m3 with forecasts that this will continuously rise steadily13. In general, biogas consists of the major components are methane (50–70%) and CO2 (30–50%). There are various impurities with very low concentrations such as H2, O2, N2, NH3, H2S, and H2O vary depending on the feedstock14. Directly converting biogas is regarded as a simple and eco-friendly approach because it is not only the best management approach for the enormous amounts of bio-waste produced domestically15, but it is also a potential pathway for converting high levels of methane and carbon dioxide into more value-added products. The dry reforming reaction (DRM) consumed methane and carbon dioxide resulting in the formation of synthesis gas having a ratio of hydrogen to carbon monoxide close to unity16, which can be practically used as a raw material in the Fischer–Tropsch industry to produce a variety of other chemicals platform17,18,19. Meanwhile, during the dry reforming reaction, a part of methane in biogas is consumed in a side reaction known as catalytic decomposition of methane (CDM) (Eq. (4)) to produce carbon nanotubes. This occurs is another advantage of processes due to carbon nanotubes (CNTs) being perceived as valuable carbon nanomaterials, as it possesses a unique for example, excellent structural, physical, electrical, and mechanical properties, resulting in a wide range of applications20,21,22,23. In this work, we focused on the integrative process of dry reforming of methane (DRM) and catalytic decomposition of methane (CDM) to establish a potential process for completely converting biogas into syngas and CNTs. Generally, the obtained CNTs are considered a main product, while the spent catalyst is impurity. In the CNT purification process, the remaining catalyst can be removed by acid leaching, then the high purity CNTs are obtained. The catalysts dissolved as ions, and it might be recovered. A wiser option is to increase a fraction of carbon to be more than 90%. It is referred to commercial grade CNTs, and it can be used as synthesized without any further purification.
An efficient dry reforming catalyst must be thermally stable and yield optimal conversions. It must also be commercially viable so that it can be scaled up for industrial applications at an affordable cost. Catalyst is considered one of the crucial important factors in achieving the conversion rate of methane and carbon dioxide for dry reforming of methane (DRM) and catalytic decomposition of methane (CDM) as well as significant influences on the yield and the morphology of the synthesized CNTs. Noble (Rh, Ru, Pd, Pt, etc.) and Non-noble (Ni, Co, Fe, etc.) metal catalysts are typically carried out over transition, and noble metal-based catalysts. Nobel metal catalysts exhibit preferable a high catalytic activity and stability, anyhow the extremely high price hinders their further development and widespread use24,25,26,27. Non-noble metal catalysts have thus attracted much attention as low-cost materials and high activity28. Among the non-noble metal catalysts, Ni exhibits the most active catalyst for dry reforming of methane (DRM) and catalytic decomposition of methane (CDM) reaction29,30,31,32,33. However, the rapid deactivation during reaction due to metal particles encapsulated by carbon and sintering under operation at high temperature is a major drawback of Ni nanoparticles34,35,36,37. Numerous studies have been conducted to overcome the problem of Ni nanoparticles by modifying the catalyst and adding second metals as promoters38,39. Mo is regarded as one of the most studied introduced for methane decomposition due to Mo in the catalysts enhancing the stabilization and dispersion of active Ni particles40. Rastegarpanah et al.41 investigated that the addition of 10% Mo raised the catalytic activity and durability of 55% Ni/MgO catalysts when compared to the unmodified catalyst. Besides the use of a second metal to combine their individual advantages, we previously investigated the effect of introducing third metal on the performance of the catalysts and the properties of the synthesized CNTs compare with bi-metallic catalysts42. The studies were carried out over NiMo/MgO, CoNiMo/MgO, FeNiMo/MgO, and CoFeMo/MgO. According to our studies, we observed that the use of bimetallic (NiMo/MgO) catalyst has outstanding catalytic performance. The high yield of CNTs with the best morphology, purity, and textural properties than the use of trimetallic catalysts were obtained. The addition of CO2 into the process can maintain the catalyst stability, compared to the decomposition of pure methane or other hydrocarbons. For example, in comparison to the direct decomposition of C2H6 for carbon nanotube (CNT) production, the presence of CO2 significantly improves the catalyst stability43. CO2 serves dual functions in CNT synthesis. When reacting with C2H6, it enhances catalyst stability and contributes to approximately 30% of the CNT production yield. The CNTs can be simultaneously produced at high CNT purity. The process can produce the value-added products in both gaseous products and solid products. CNTs can be applied for many applications, such as batteries, supercapacitors, electronics, adsorbent, and reinforced materials44. In addition, biogas can be used without any CO2 separation. Cao et al.45 found that the enhanced CO2 adsorption is crucial for coke gasification, with promoted catalysts showing lower coke yields, compared to the pristine material. The morphology of coke impacts the catalyst deactivation. The amorphous coke has minimal effect, while the graphitic carbon, such as carbon nanotubes, significantly impairs the activity by encapsulating active metals. Charisiou et al.46 reported that the spent Ni/Al samples shows a large coke formation, especially in the less basic alumina-based materials. This indicates a faster methane decomposition and carbon polymerization process, compared to the CO2 activation. However, carbon formation and gasification rates show similar on more basic Ni/LaAl catalysts, with coke deposits as nanotubes on Ni particles.
As a continuous work, this work aims to develop the integrative process of dry reforming (DRM) and catalytic decomposition of methane (CDM) to optimize reaction temperature for the utilization of biogas to completely convert into syngas and carbon nanotubes. This experiment was carried out over a NiMo/MgO catalyst using purified biogas at a fixed ratio of CH4/CO2 (60/40), which is considered a typical composition47,48. The raw biogas usually contains approximately 50–70% CH4 and 30–50% CO2, humidity, and traces of H2S, N2, H2, depending on the sources of feedstock49,50. It accepted that the composition consisting of 60% CH4 and 40% CO2 represents a typical ratio of CO2/CH4 in biogas50. In addition, the effects of varying ratio of CH4/CO2 on growth and structure of carbon nanotubes are investigated. The long-term stability under optimization of reaction temperature and the ratio of CH4/CO2 was performed. The obtained CNTs are thoroughly characterized by various techniques.
Experimental
Catalyst preparation
The bimetallic NiMo catalyst supported on MgO was synthesized by the wetness impregnation of two metal precursors: Ni(NO3)2·6H2O and (NH4)6Mo7O24·4H2O (Sigma Aldrich) with mass ratio of 1:1. The total metal loading of Ni and Mo was set at 30 wt%. Briefly, the calculated metal precursor was dissolved in distilled water until formed a completely clear solution. Further, the solution was dropped into MgO nano-powder (98%, Panreac AppliChem) and stirred at room temperature. After a homogeneous slurry formed, the mixture was evaporated on a hotplate at 80 °C until dried catalyst powder was obtained. The resultant powder was then calcined in a muffle furnace at 500 °C for 3 h with a ramp rate of 10 °C/min.
Characterization
The crystallinity and crystalline phases of both reduced and spent catalysts were examined by X-ray diffraction (XRD, Bruker, D2 Phaser). The XRD patterns were recorded with diffraction angles 2θ ranging from 10° to 80°. The elemental component of reduced catalysts was determined by X-ray fluorescence (XRF, S8 TIGER, Series 2). The morphology of synthesized CNTs was observed by field-emission scanning electron microscope (FE-SEM, JEOL, JSM-7610F). The internal structure of synthesized CNTs was characterized by field-emission transmission electron microscope (FE-TEM, JEOL, JEM-3100, Japan) at acceleration voltage of 300 kV. The number of walls and interlayer spacing are analyzed from TEM images using ImageJ software. The graphitization of synthesized CNTs were evaluated using Raman spectrophotometer (PerkinElmer® SpectrumTM GX). The purity of the synthesized CNTs analyzed by thermogravimetric analysis (TGA, Mettler Toledo, TGA/DSC1). The sample was heated from room temperature to 800 °C, at heating rate of 10 °C/min under O2 flow of 100 ml/min. The textural properties of the synthesized CNTs was analyzed by N2 sorption measurement (Micromeritics, TriStar II 3020). The sample was degassed under N2 flow at 150 °C for 4 h. The specific surface area was calculated using Brunauer–Emmett–Teller (BET) method, whereas the pore size distribution was estimated according to the Barrete–Joynere–Halenda (BJH) using the desorption isotherm data.
Catalytic evaluation
All catalytic performance tests were conducted under atmospheric pressure in the horizontal tubular quartz (2.53 cm inner diameter and 110 cm long) heated by tube furnace, as schematically shown in Fig. 1. A quartz boat (dimension W/H/L: 2/3/10 cm) containing a certain amount of catalyst power was located at the center of the reactor. The catalyst power occupies only the half lower space of cross-sectional area of reactor tube. The space is leaving for CNT growth, avoiding plugging the reactor tube. However, the reaction gases thoroughly diffuse into the sublayer and the bottom bed of the catalyst. This packing of catalyst is a common practice for CNTs production in a fixed bed reactor. The catalyst was first activated by H2 reduction process, heated from room temperature to 1000 °C with a ramp of 10 °C/min under H2 flow of 75 ml/min. Then, the reactor was set to the designate reaction temperatures, and the model biogas (60% CH4 and 40% CO2, CH4/CO2 = 1.5/1) was introduced to the reactor at 400 ml/min across 0.5 g of NiMo/MgO, corresponding to GHSV = 48,000 ml/g-h. The reaction time was set for 3 h, and during the reaction, the composition of effluent gases was analyzed at regular intervals (10 min) by gas chromatography (TCD, Shimadzu, GC-2014). Finally, after ending the reaction, helium gas was turned into the reactor, while the reactor was cooled down to room temperature. The carbon product together with spent catalyst was collected and kept for further characterization.
This work investigates the effects of reaction temperature, CH4/CO2 ratio, and catalyst durability. The reaction temperature was studied at 700, 800, 900, and 1000 °C, while CH4/CO2 ratio was studied at 1.5/1, 1/1, and 0.5/1 at 800 °C. The catalyst durability was tested with the condition: CH4/CO2 1.5/1, GHSV = 48,000 ml/g-h at 800 °C for 20 h. However, the initial weight of catalyst was reduced to 0.25 g with a biogas flow of 200 ml/min. The catalytic performance of catalyst was evaluated by conversions of reactants and product yields (syngas and CNTs). The methane conversion (XCH4) and carbon dioxide conversion (XCO2), and syngas purity were calculated using Eqs. (5)–(7).
where, [i]in and [i]out represents the concentration of reactant gas (CH4, CO2) or product (CO, H2) flowing into and out of the reactor. Fin and Fout refer to the total volumetric gas flow rate of the inlet and outlet from the reactor (ml/min). Fi represents the flow rate of each gas species.
In this work, we present CNT productivity in two ways: The CNT productivity was evaluated based on the CNT gram yield and percent carbon yield using Eqs. (9, 10). The gram yield represents the productivity with respect to catalyst, while percent carbon yield indicates the CNT productivity with respect to carbon source. CNT purity was calculated by Eq. (11). The gas hourly velocity (GHSV) was calculated based on Eq. 12.
where Freactant, mcatalyst, and mproduct represent the volumetric flow rate of reactant gas, the weight of the reduced catalyst, and spent catalyst including carbon formation, respectively.
Results and discussion
Characteristics of NiMo/MgO catalyst
The physicochemical properties of as-prepared NiMo/MgO catalyst including elemental composition, crystallinity, and reducibility were analyzed. Table 1 shows the elemental composition of reduced NiMo/MgO catalyst determined by X-ray fluorescence (XRF) and Inductively Coupled plasma (ICP-OES)42. It was observed that the total metal loading is 31.8–31.9 wt%, while the mass ratio of Ni to Mo is 0.97–1.07. The results are consistent with the predetermined total metal loading of 30 wt%, and the mass ratio of 1/1, confirming the accurate procedure of catalyst preparation.
Crystalline phases of fresh catalysts after being treated in the calcination and the reduction processes were identified by X-ray diffraction (XRD), and the results are depicted in Fig. 2. It was found that the existences of predominant peaks at 2θ = 37, 43, 62, 75, and 78°, which assigned to the (111), (200), (220), (311), and (222) crystal planes of MgO (JCPDS #45-0946) were detected in both calcined and reduced catalysts. In Fig. 2a, the calcination of Mo in the air atmosphere at 500 °C led to the formation of the molybdenum oxide phase (MoO3, JCPDS #05-0508), generating the broad reflection peaks (2θ = 23°, 27°, 34°, and 48°). Besides, MgMoO4 phase at 2θ = 18° (JCPDS #72-2153) formed by the interaction between MoO3 and MgO at temperatures above 400 °C51, also appeared with low crystallinity. On the other hand, the characteristic peak of NiO phase (JCPDS #47-1049) was almost absent or undetectable. The reason is probably owing to NiO being well dispersed, corresponding to the introduction of Mo in the catalyst favors the dispersion of Ni52. In addition, the absence of Ni2+ in Fig. 2b confirmed the dispersion of the Ni–MgO solid solution, causing the peak at 43° to shift to a lower 2θ value which is consistent with the XRD pattern from a previous study53. The XRD patterns of reduced catalysts shown in Fig. 2b, it shows no apparent patterns of their metal oxides, indicating that they had been converted into metallic Ni and Mo phases throughout the H2 pretreatment process. After reducing the catalyst at 1000 °C, we observed no evidence of MgO sintering. This is likely because MgO nano-powder has closely packed ions, resulting in a high sintering temperature54. In addition, Saconsint et al. reported that NiMo can stabilize the crystallite size of MgO at 18.1 nm during the reduction process, while the reduction of MgO showed a larger crystallite size of 24.1 nm42.
Figure 3 shows the H2-TPR profile of NiMo/MgO catalysts. The fresh catalyst was calcined at 500 °C for 3 h. It was found that the reducibility of catalyst exhibits a broad region between 400 and 1000 °C with four distinct peaks at 422 °C, 547 °C, 697 °C, and 799 °C. The small sharp peak at 422 °C indicates the presence of reducible Ni2+ with moderate and mild strength interaction to the support. The second sharp peak at located at 547 °C is ascribed to the reduction of NiO species with strong interaction the support55. At 600–1000 °C, the two peaks at 697 and 799 °C, indicating (I) the reduction of Mo6+ to Mo4+ and the first reduction step of MgMoO4, and (II) the second reduction step of MgMoO4 and the reduction of Mo6+ to metallic Mo0. Therefore, the catalyst was intentionally reduced at relatively high temperature of 1000 °C, according to the H2-TPR results for the complete reduction.
Effect of reaction temperature on NiMo/MgO catalytic performance
Figure 4 presents the test results of catalytic performance of NiMo/MgO catalyst expressed by CH4 conversion, CO2 conversion, and H2/CO ratio as a function of time on stream (TOS) at different reaction temperatures of 700, 800, 900, 1000, and 1100 °C, while the summary of syngas and CNT products is provided in Table 2. The effects of reaction temperature show that as the temperature elevated from 700 to 900 °C, conversion of both CH4 and CO2 significantly increased (Fig. 4a,b). Basically, high temperature accelerates the conversion rate of endothermic reactions: dry reforming (\(\Delta{\text{H}}_{\text{298K}}^{\circ}= +247 \text{ kJ mol}\)) and methane cracking (\(\Delta{\text{H}}_{\text{298K}}^{\circ}= +75.3 \text{ kJ mol}\)). Further increase in temperature from 900 to 1100 °C, however, would slow down the conversion rates. This result implies that catalyst deactivation appeared at high temperature. High temperature induces migration of Ni-Mo particles, resulting in agglomeration and metal sintering. Notably, more severe catalyst deactivation was observed in low temperature side at 700 °C. The conversion rates rapidly decreased from approximately 60–80% to nearly zero within 3 h TOS. In contrast to high temperature side, the catalyst suffered from carbon deposition at lower temperature. It is apparent that carbon deposit on the spent catalyst at 700 °C, exhibits unique characteristic: low graphitic ratio (Ig/Id = 0.76) and higher deposition temperature (~ 700 °C) (see Fig. 7 and Fig. 8). Even though the amount of deposit carbon only 17.1% compared to other reaction temperatures (84.0, 83.7, 54.9% for 800, 900, 1000 °C), it shows great negative impact on catalyst performance.
Herein, considering the gaseous and solid products of reaction, behaviors of changing syngas and CNT yields (Table 2) are consistent well with the conversion rates as discussed above. Specifically, the temperature elevated (700–900 °C) enhanced overall production yields, while the excessive high temperature (900–1100 °C) reduced the rates of product formation. As a result, yields of syngas and CNTs were maximized at temperatures of 800–900 °C.
It should be noted that CNT yield is highly sensitive to the reaction temperature. The highest CNT yield of 2.60 gProduct/gCat-h was achieved at 800 °C. However, the yield of CNTs was significantly decreased, as the reaction temperature was further increased above 900 °C. At such high temperatures, the dissolving rate of carbon species on catalyst surface would be higher than the rates of diffusion and precipitation, resulting in the accumulation of carbon atoms on the catalyst surface and loss in its activity56. Moreover, the high temperature would accelerate the sintering of catalyst particles, leading to loss of activity. As a result, it was concluded that the optimum temperature for the synthesis of CNTs was carried out at 800 °C.
Considering the gaseous products, it was found that the high temperatures (900–1100 °C) would result in a decrease in both syngas yield (Table 2) and H2/CO ratio (Fig. 4c). The former was caused by the catalyst deactivation, while the latter was due to, at high temperature, dry reforming (CO2 + CH4—> 2CO + 2H2) was pronounced more than methane cracking. Additionally, the high temperature would promote endothermic reverse water gas shift reaction (Eq. (13)), in which the H2 is consumed to produce CO and H2O57.
Among the investigated temperatures, it can be concluded that the reaction at 800 °C could be appropriate temperature for simultaneously producing syngas and CNTs at high yields, as well as maintaining best catalyst stability over 3 h TOS. Although the temperature at 900 °C could provide the highest conversions of CH4 and CO2 at 90.10% and 98.97% and the highest syngas purity of 93.9%, the conversion rates gradually decreased after 40 min TOS, indicating catalyst deactivation.
Effect of reaction temperature on CNT characteristics
The characteristics of CNTs synthesized over NiMo/MgO catalysts at different temperatures, including morphology, internal structure, crystallinity, graphitization, purity, and textural properties were examined by SEM, TEM, XRD, Raman, TGA, and BET analyses. Figure 5 presents SEM images, TEM images, and corresponding diameter distribution of synthesized CNTs over NiMo/MgO catalyst at different temperatures; 700, 800, 900, 1000, and 1100 °C. It is evident that the carbon formed on all catalyst tests consisted of entangle nanofilaments with several graphene layers that are known as multi-walled carbon nanotubes (MWCNTs). Denser MWCNTs were observed over the catalyst surface under temperatures of 800 °C and 900 °C, corresponding to the high resultant yield of carbon received at these operating conditions.
Considering surface morphology and shape of CNTs elucidated by SEM, low temperature side (700–900 °C) produced a distorted/bent nanotube with rough surface, while high temperature side (1000–1100 °C) resulted in more straighter nanotubes with smoother surface. In addition, the length of the tubes become longer, and fewer defects were observed at the outer wall.
Table 3 summarizes the key morphological characteristics of CNTs synthesized over NiMo/MgO catalyst at different temperatures. The diameter distribution, average diameter (dav) of the synthesized CNTs measured from several SEM images, as well as the number of wall and the interlayer spacing derived from TEM results. These revealed that CNTs produced at temperatures between 700 and 900 °C show a morphological similarity in terms of primary diameter size (dav = 23–24 nm), diameter size distribution, number of walls, interlayer spacing, and surface morphology. Interestingly, the CNTs produced at 800 °C are not only the highest yield, but also possess the narrowest diameter size distribution with standard deviation of 4.4 nm. Surprisingly, at 1000 °C the CNTs has the smallest diameter of 15.8 nm with larger interlayer spacing of 0.37 nm. Basically, the interlayer spacing is influenced by CNT diameter and the symmetry of layers58. At 1100 °C, agglomeration of metal particles began to be obvious, resulting in the larger and wider diameter of CNTs59. It is concluded that the reaction at 800 °C shows the optimum temperature for production of CNTs at high yield and uniform diameter.
Figure 6 presents the XRD patterns of the solid products over NiMo/MgO catalyst after reaction at different temperatures. Compared to the XRD pattern of the fresh reduced catalysts, it is obvious that the reflection peak at 2θ = 26.1° was signified the (002) lattice plane of graphitic carbon materials appeared in all samples. Especially for the diffraction pattern that was performed under temperatures of 800 °C has the highest intensities, which represented the yield of carbon on the spent catalyst, where high catalytic activities for producing carbon nanomaterials display a strong peak. Furthermore, this peak can be used to quantify the level of crystallinity in terms of interplanar spacing as well, d002, which is calculated via Bragg’s equation60 and illustrated in Table 4. It was found that all the used catalysts have produced the CNTs with the inter shell spacing value of approximately ~ 0.346 nm, which is even closer to the value of graphite structure (0.335 nm). This shows that flame high-quality crystalline structure of CNTs was grown over the spent catalysts and somewhat improved as the deposition temperature increased. This is also in agreement with the other results obtained in many studies61,62,63. In addition, the diffraction peaks located at 2θ = 42.9° were detected in all samples, where generally attributed to the crystallinity of graphitic carbon as well. However, these peaks overlap with the characteristic peak assigned to MgO support, that is made it difficult to separate peaks. Thus, the relative intensity of this peak does not necessarily indicate the qualitative structural properties of as-grown CNTs.
The graphitization of all synthesized CNTs produced onto NiMo/MgO catalyst at different temperatures was analyzed by Raman spectroscopy as shown in Fig. 7. The G-band (observed at 1500–1600 cm−1) is related to the tangential stretching mode of all pairs of sp2 atoms in both rings and chains which represents the graphitic carbon structure, while D-band (observed at 1300–1400 cm−1) is associated with the structural defect and impurity which represents the disordered carbon or amorphous carbon with deposited on the outer surface of carbon nanotube. The quality of carbon nanotube is indicated by the intensity ratio between G-band and D-band (Ig/Id), which higher value (> 1) indicates a good degree of graphitization with fewer defects of carbon nanotube. The results from Raman analysis shows that all synthesized CNTs (Ig/Id = 0.76–3.69) presented Ig/Id ratio higher than commercial CNTs (Ig/Id = 0.74). Apparently, G-band's relative intensity to D-band (Ig/Id) was achieved when the reaction temperature was high as shown in Fig. 7, indicating that a better-graphitized of CNTs was obtained. This occurrence could be ascribed that increases in reaction temperature can increase the solubility of carbon in metal catalysts contributing to the formation of CNTs with greatly graphitized wall structures59. This was consistent with the TEM results as shown in Fig. 5 as mentioned above. However, the remarkable decrease in the graphitization at 1100 °C, may be due to the operation under high temperature causing the sintering of metal catalysts leads to lost activity.
Compared to other studies, Charisiou et al.46 found that both Ni/Al and Ni/LaAl catalysts show that the CNTs contain some defects including amorphous carbon and 16 graphitic layers. However, the high IG/ID ratio of 2.86 at 800 °C indicates a high quality of CNTs with a significant graphitic structure. Another research study also supports these findings4 suggested that a high IG/ID ratio can be achieved at 800 °C despite the presence of some defects. These defects can be reduced by narrowing the D' band. Along with similar reports support these findings64 shows that temperature of 750 °C provide high IG/ID. However, some defects also present in CNTs structure. Pawar et al.65 proposed that higher temperature could lead to higher carbon nano-structure deposit on Ni/γAl2O3 catalyst along with increase CH4/CO2 ratio in comparison.
Figure 8 illustrates the TGA curves of CNTs products synthesized under varied reaction temperatures. From the TGA analysis, all samples exhibited the same oxidation behavior with a single-step degradation, and no apparent weight loss was observed at temperatures below 400 °C. This may be attributed to their high degree of structural order since the appearance at higher inflection temperature can provide a better crystallinity and thermal stability of MWCNTs66,67. In many previous studies, it has also been reported that the percentage of weight loss can refer to the carbon yield in the catalysts that occurs during the oxidation of deposited carbon with oxygen68. The purity of CNTs, measured by TGA is presented in Table 2. For temperatures at 800 °C and 900 °C, it is obvious that the small amounts of residue catalyst weight are nearly close to each other, reflecting the improvement of carbon formation with a high purity produced under these reaction conditions, which correlates to the result determined by SEM observation (Fig. 5). Even operating in this region can give better thermal stability with the highest graphitization degree of carbon nanotubes, it seems to show some of the remaining catalysts in the sample, suggesting that it has not able enough to remove the rest of the residual catalysts when compared to the commercial CNTs ones, as displayed in Fig. 8.
N2 sorption measurement is used to assess the textural properties of all synthesized CNTs at different reaction temperatures over NiMo/MgO catalyst, and the results are listed in Table 5 and shown in Fig. 9. It was found to be the specific surface area (SBET), mesopore volume (Vmeso), total pore volume (Vtotal), and average pore diameter (Davg) of synthesized CNTs decreased as the temperature decreased. In Table 5, it can be indicated that all synthesized CNTs are due to the mean pore size of synthesized CNTs being in 11–15 nm which is in the range of mesopore material (2–50 nm). It also confirms by N2 absorption–desorption isotherms of all synthesized CNTs shown in Fig. 9a, present type IV isotherm according to IUPAC classification. The hysteresis loops formed by the capillary condensation effect can be classified as H3 hysteretic loop, usually found in solids consisting of aggregates or agglomerates of particles forming slit-shaped pores, with a non-uniform size and/or shape. The pore diameter distributions based on the BJH method as shown in Fig. 9b present the curves, which can be ascribed that all the synthesized CNTs exhibit a bimodal feature which has a pore size with a board distribution ranging from 2 to 140 nm, including a small pore-size fraction (2–4 nm) and a large pore-size fraction (4–150 nm).
Effect of biogas composition
Generally, the composition of biogas depends on the nature of the material used69. The ratio of CH4 and CO2 in biogas is considered as an important factor in the integration process of DRM and CDM reactions, which may affect the syngas (H2 + CO) and CNTs production. In this part, we investigated the effect of the biogas ratio with a variation of CH4/CO2 in 1.5/1, 1/1, and 0.5/1, which was tested for 3 h. The reaction temperature of 800 °C was selected for carrying out this experiment, based on the previous discussion to identify the optimum condition. The effluent gas composition of outlet stream as a function of times on stream over 3 h. is shown in Fig. 10. In Fig. 10, the biogas using CH4/CO2 ratio of 1.5/1 achieved higher CH4 and CO2 conversion of 86.44% and 95.62%, respectively. The existence of an excess of CH4 in the feed stream is likely to have produced favorable conditions for the integration of DRM and CDM processes. However, the high concentration of CO2 attenuated the CH4 and CO2 conversion, but it also remains stable over the study time. As a general, DRM reaction is required the CH4/CO2 ratio of 1/1 based on stoichiometry in Eq. (1) for producing syngas (H2 + CO). In this investigation, we found that a CH4/CO2 ratio of 1.5/1 is more favorable for producing syngas under the study conditions, which contributed to a higher H2/CO ratio of 1.1 and syngas purity of 90.04%. The effect of varying biogas feed concentration on the CNTs yield is demonstrated in Fig. 11. One prominent trend is clearly noteworthy that the CNTs yield attained an increase with increasing CH4 content in Biogas, implying that a high amount of CH4 is sufficient to promote producing CNT through CDM reaction. Therefore, the biogas with CH4/CO2 ratio of 1.5/1 provided the highest CNTs yield of 2.60 gProduct/gCat-h. As a result of these observations, it was suggested that the biogas used with less CH4 content may be unsuitable for simultaneously produced syngas and high value-add carbon nanomaterial.
To study the influence of biogas composition, the reaction was carried out at different ratio of CH4/CO2 from 0.5 to 1.5. The CNTs formed were investigated under FE-SEM and HR-TEM analysis as depicted in Fig. 12. It was clearly observed that the growth of nanotubes are multi-walled CNTs, which were densely presented on the use of the CH4/CO2 with the highest ratio of 1.5 (Fig. 12a) while the extremely tiny amount of carbon nanotubes was detected only at the edge of the catalyst with a feed ratio of CH4/CO2 equal to unity and becoming even less or absent when the level of carbon dioxide continuously raised (that is, CH4/CO2 = 0.5/1) (Fig. 12b,c). According to these findings, it can be implied that increasing the concentration of CO2 in the inlet reactant gases decreased the presence of carbon nanomaterial, conversely, inserting more CH4 content can promote the growth of CNTs as observed in the yield carbon results. This is probably due to the highly stable of CO2 and thus causing it difficult to crack carbon atoms for forming to be solid carbon as a co-product70. Furthermore, at the largest amount of feeding CO2, it appears obvious that the textural of the catalyst had changed slightly compared to the fresh catalyst before running the reactions as demonstrated in Fig. 13. The CO2 oxidation under this circumstance (CH4/CO2 ratio of 0.5/1) led to a catalyst surface composed of some hexagonal microrods which evidently appeared in the inset SEM image (Fig. 13b) that shows the zoom-in view for the surface morphology of catalyst. This suggests that there is one another form of molybdenum oxide phase (MoO3)71, which is expected to be an explanation for the absence of CNTs in the sample.
From a previous discussion, the arising of the oxide species under varied conditions was further examined using the XRD technique and the results are shown in Fig. 14. Obviously, upon continuing to increase the amount of CO2 in the feed line, several diffraction peaks attributed to MoO2, MoO3, and NiMoO4 were detected at different two theta positions, whereas the Mo2C phases disappeared once the feed CH4/CO2 ratio was reached to 0.5/1 (Fig. 14d), suggesting that Mo2C could be readily oxidized by CO2 and then converted into an inactive MoO2 phase and CO. Adrianne et al.72 stated that MoO2 phases causing the gradual catalyst deactivation and the results clearly shown no coking after that. Nonetheless, in our study, it is quite worthy to note that even though the characteristic peaks of MoO2 phases are detected in the XRD pattern, the conversions exposed in Fig. 10 are remarkably constant and the catalyst seems not to deactivate at all. Moreover, MoO2 can be further oxidized into MoO3 with CO2 atmosphere, this appears evident that MoO3 oxide phases have been widely distributed on the surface of the catalyst, which is in accordant with more micro-rods of molybdenum oxide observed in SEM analysis (Fig. 14d). Besides, it has been reported that the deposited carbon dynamically varied with MoOx species because of its strong ability to allow the lattice oxygen (O*) to oxidize and remove the carbon formed during the DRM reaction52. This is also responsible for the absence of CNTs in this sample. Based on these results, we can conclude that the higher concentration of carbon dioxide in the entering gas, the less MWCNTs can be obtained.
It was also found that the main graphitic reflection peak at 2θ = 26.1° is predominant and even more dominant in the diffraction profile of the first sample test under a feed ratio of CH4/CO2 measured up to be 1.5 over the remaining peaks that reflected carbide, metallic, or other phases else. This can be indicated that the catalyst used under the condition mentioned earlier has superior performance to accumulate carbon nanomaterials and higher quality of deposited carbon can be achieved as illustrated in Fig. 14b.
The Raman spectra and the trend of Ig/Id ratio of synthesized CNTs obtained over NiMo/MgO catalyst at 800 °C using varied biogas ratios (CH4/CO2) of 1.5/1, 1/1, and 0.5/1 are shown in Fig. 15. The results present the Ig/Id intensity ratio of all synthesized CNTs (Ig/Id = 0.87–1.27) higher than commercial CNTs (Ig/Id = 0.74), which meant that the synthesized CNTs have a high quality. Noticeably, G-band's relative intensity to D-band (Ig/Id) is high in the CNTs synthesized using biogas at low CO2 content whereas it gradually decreases with the further increase of CO2 content in biogas. This tendency may principally be attributed to the oxidation effect of CO2 reacting with the graphitic layer in CNTs under operation at 800 °C73, leading to less structure quality of the CNTs.
Durability of NiMo/MgO catalyst
Based on the previous results, the stability test of NiMo/MgO was carried out to probe the catalyst's longevity using a biogas ratio (CH4/CO2) of 1.5/1 over 20 h, as shown in Fig. 16. In Fig. 16, the catalyst was noticeably deactivated during the first 6 h of reaction with the methane and carbon dioxide conversion decreased from 92.98% and 98.04% to 79.27% and 96.51%, respectively. Afterward, the catalytic performance was stable with a slight deactivation comparable to a 7.44% and 3.27% loss in methane and carbon dioxide conversion. The point of view of this behavior can be attributed that the catalyst being initially exposed to the reactant gas resulting in CNTs growth. Over time, the numerous entangled CNTs structure network covered the catalyst surface, hindering the diffusion of methane and carbon dioxide toward the catalyst particles. This appearance asserted by methane and carbon dioxide greatly loss on the conversion as clearly perceived in the deactivation zone. After the reaction proceeds into the nearly constant zone, the CNTs production was continuously growing with a low formation rate compared to the deactivation zone due to a decreased surface of active metal attenuated methane and carbon dioxide decomposition rate. The CNTs production gradual growth may cause the catalytic performance to exhibit excellent stability. It can be speculated that it might exhibit stability with a reaction time of more than 20 h. This finding reinforces the notion that NiMo/MgO is an effective catalyst for biogas upgrading through the combination of dry reforming and catalytic breakdown of methane (CDM).
Figure 17 presents FE-SEM, HR-TEM micrographs, and diameter distribution curves of carbon deposited over NiMo/MgO catalyst, which were later collected for characterization after the reaction at 800 °C with varied from 3 to 20 h time on stream. Apparently, all catalytic tests in this study produced a highly carbonaceous density of multi-walled CNTs. On top of that, it can be observed that some metal catalyst particle is embedded at the end of nanotubes as depicted in some white portion areas, which confirmed the formation of carbon nanotubes via the typical tip-growth mechanism74,75. These areas began to fade intensely away once reaction time was continually raised, demonstrating that the catalyst was being lifted off from the support material and elongated to form carbon nanofilament more and more, resulting in a high yield of solid carbon products. Moreover, no amorphous carbons were observed on the sidewall of tubular MWCNTs structure. This indicates that the produced CNTs in the 20 h time on stream test possess a greater degree of graphitization order. In addition, the length of MWCNTs seems to keep growing as much longer as time goes by.
The average diameter, the standard deviation, as well as the number of walls for the as-grown CNTs are calculated from SEM and TEM images, respectively, and be listed in Table 6. It is surprising to observe that an obvious decrease in the diameter nanotube was formed at a longer reaction time with a lower total inlet flow rate and amount of catalyst at half of usual that were applied for 3 h (200 ml/min and 0.25 g). The appropriate description for this finding is that the concentration of reactant gases per surface area is relatively low, and the catalyst layer was slightly thin. Thus, the carbon atoms were then distributed towards the catalyst particles in low magnitude. The carbon is easily diffused through the bottom layer. Consequently, large quantities of MWCNTs with small diameters can be obtained. On the other hand, at a higher feed flow rate with a very thick layer of the catalyst bed together, a huge number of carbon atoms are deposited intensely on the catalyst surface, leading to the aggregation of carbon species around metal particles, and therefore corresponds to enlarging of catalyst particle dimension and later holding somewhat larger diameter CNTs76,77.
Conclusion
This work has investigated the influence of process parameters on the catalytic performance of NiMo/MgO catalyst for converting biogas into syngas and carbon nanotubes. Multi-walled carbon nanotubes (MWCNTs) with the smallest diameter and the highest graphitization can be produced at 1000 °C. However, at higher temperature of 1100 °C, the agglomeration of metal particles due to the sintering was observed, resulting in the larger and broader diameter distribution of CNTs. Interestingly, the highest carbon yield and the uniform CNT diameter can be achieved at 800 °C as the optimum temperature, being a promising condition for mass production with low energy consumption. In addition, the catalyst can perform well with high stability more than 20 h at 800 °C. The effect of biogas composition was examined. The typical biogas composition of CH4/CO2 of 1.5 showed positive results in terms of enhancing production yields of CNT and syngas with negligible drop in the catalyst activity. Although the high fraction of CO2 in biogas caused the formation of MoO3 species, the catalyst activity was unchanged. The combination of Ni and Mo shows the synergistic property and suitable composition for utilizing in the biogas conversion at the various temperatures and gas compositions.
Data availability
All data related to the finding of this study are accessible upon request from the corresponding author Sakhon Ratchahat.
References
Abdulrasheed, A. et al. A review on catalyst development for dry reforming of methane to syngas: Recent advances. Renew. Sustain. Energy Rev. 108, 175–193 (2019).
Akri, M. et al. Atomically dispersed nickel as coke-resistant active sites for methane dry reforming. Nat. Commun. 10(1), 5181 (2019).
Aramouni, N. A. K., Touma, J. G., Tarboush, B. A., Zeaiter, J. & Ahmad, M. N. Catalyst design for dry reforming of methane: Analysis review. Renew. Sustain. Energy Rev. 82, 2570–2585 (2018).
Charisiou, N. D. et al. An in depth investigation of deactivation through carbon formation during the biogas dry reforming reaction for Ni supported on modified with CeO2 and La2O3 zirconia catalysts. Int. J. Hydrogen Energy 43(41), 18955–18976 (2018).
Pakhare, D. & Spivey, J. J. A review of dry (CO2) reforming of methane over noble metal catalysts. Chem. Soc. Rev. 43(22), 7813–7837 (2014).
Song, Y. et al. Dry reforming of methane by stable Ni–Mo nanocatalysts on single-crystalline MgO. Science 367(6479), 777–781 (2020).
Yentekakis, I. & Dong, F. Grand challenges for catalytic remediation in environmental and energy applications toward a cleaner and sustainable future. Front. Environ. Chem. 1, 5 (2020).
Yentekakis, I. V. et al. Effect of support oxygen storage capacity on the catalytic performance of Rh nanoparticles for CO2 reforming of methane. Appl. Catal. B Environ. 243, 490–501 (2019).
Zhang, G., Liu, J., Xu, Y. & Sun, Y. A review of CH4CO2 reforming to synthesis gas over Ni-based catalysts in recent years (2010–2017). Int. J. Hydrogen Energy 43(32), 15030–15054 (2018).
Ross, J. R. H. Natural gas reforming and CO2 mitigation. Catal. Today 100(1), 151–158 (2005).
Obrecht, M. & Denac, M. Biogas—A sustainable energy source: New possibilities and measures for Slovenia. J. Energy Technol. 4, 11 (2011).
Jung, S., Lee, J., Park, Y.-K. & Kwon, E. E. Bioelectrochemical systems for a circular bioeconomy. Bioresour. Technol. 300, 122748 (2020).
Scarlat, N., Dallemand, J.-F. & Fahl, F. Biogas: Developments and perspectives in Europe. Renew. Energy 129, 457–472 (2018).
Vita, A., Pino, L., Cipitì, F., Laganà, M. & Recupero, V. Biogas as renewable raw material for syngas production by tri-reforming process over NiCeO2 catalysts: Optimal operative condition and effect of nickel content. Fuel Process. Technol. 127, 47–58 (2014).
Yentekakis, I. V. & Goula, G. Biogas management: Advanced utilization for production of renewable energy and added-value chemicals. Front. Environ. Sci. 5, 7 (2017).
Bradford, M. C. J. & Vannice, M. A. CO2 reforming of CH4. Catal. Rev. 41(1), 1–42 (1999).
Gadalla, A. M. & Sommer, M. E. Synthesis and characterization of catalysts in the system A12O3-MgO-NiO-Ni for methane reforming with CO2. J. Am. Ceram. Soc. 72(4), 683–687 (1989).
Cao, P., Adegbite, S., Zhao, H., Lester, E. & Wu, T. Tuning dry reforming of methane for F-T syntheses: A thermodynamic approach. Appl. Energy 227, 190–197 (2018).
Golestan, S., Mirzaei, A. A. & Atashi, H. Fischer–Tropsch synthesis over an iron–cobalt–manganese (ternary) nanocatalyst prepared by hydrothermal procedure: Effects of nanocatalyst composition and operational conditions. Int. J. Hydrogen Energy 42(15), 9816–9830 (2017).
Baughman, R. H., Zakhidov, A. A. & de Heer, W. A. Carbon nanotubes—The route toward applications. Science 297(5582), 787–792 (2002).
Coleman, J. N., Khan, U., Blau, W. J. & Gun’ko, Y. K. Small but strong: A review of the mechanical properties of carbon nanotube–polymer composites. Carbon 44(9), 1624–1652 (2006).
Dalton, A. B. et al. Super-tough carbon-nanotube fibres. Nature 423(6941), 703–703 (2003).
Wu, F. & Xu, B. Progress on the application of carbon nanotubes in supercapacitors. New Carbon Mater. 21, 176–184 (2006).
Abdullah, B., Abd Ghani, N. A. & Vo, D.-V.N. Recent advances in dry reforming of methane over Ni-based catalysts. J. Clean. Prod. 162, 170–185 (2017).
Chen, S. & Yang, B. Activity and stability of alloyed NiCo catalyst for the dry reforming of methane: A combined DFT and microkinetic modeling study. Catal. Today 400–401, 59–65 (2022).
Izhab, I., Asmadi, M. & Saidina Amin, N. A. Methane dry reforming using oil palm shell activated carbon supported cobalt catalyst: Multi-response optimization. Int. J. Hydrogen Energy 46(48), 24754–24767 (2021).
Yabe, T. & Sekine, Y. Methane conversion using carbon dioxide as an oxidizing agent: A review. Fuel Process. Technol. 181, 187–198 (2018).
Baraka, S. et al. Catalytic performances of natural Ni-bearing clay minerals for production of syngas from dry reforming of methane. J. CO2 Util. 52, 101696 (2021).
Amin, A. M., Croiset, E. & Epling, W. Review of methane catalytic cracking for hydrogen production. Int. J. Hydrogen Energy 36(4), 2904–2935 (2011).
Avdeeva, L. B., Reshetenko, T. V., Ismagilov, Z. R. & Likholobov, V. A. Iron-containing catalysts of methane decomposition: Accumulation of filamentous carbon. Appl. Catal. A Gen. 228(1), 53–63 (2002).
Damyanova, S., Pawelec, B., Arishtirova, K. & Fierro, J. L. G. Ni-based catalysts for reforming of methane with CO2. Int. J. Hydrogen Energy 37(21), 15966–15975 (2012).
Kawi, S. et al. Progress in synthesis of highly active and stable nickel-based catalysts for carbon dioxide reforming of methane. ChemSusChem 8(21), 3556–3575 (2015).
Rogers, J. L. et al. Differences in the nature of active sites for methane dry reforming and methane steam reforming over nickel aluminate catalysts. ACS Catal. 6(9), 5873–5886 (2016).
Fang, X. et al. Methane dry reforming over Ni/Mg-Al-O: On the significant promotional effects of rare earth Ce and Nd metal oxides. J. CO2 Util. 25, 242–253 (2018).
Ha, Q. L., Armbruster, U., Atia, H., Schneider, M., Lund, H., Agostini, G., Radnik, J., Vuong, H. T., Martin, A. Development of active and stable low nickel content catalysts for dry reforming of methane. Catalysts [Online], 2017.
Marinho, A. L. A. et al. Embedded Ni nanoparticles in CeZrO2 as stable catalyst for dry reforming of methane. Appl. Catal. B Environ. 268, 118387 (2020).
Shi, C. et al. A review of different catalytic systems for dry reforming of methane: Conventional catalysis-alone and plasma-catalytic system. J. CO2 Util. 46, 101462 (2021).
Ashik, U. P. M., Wan Daud, W. M. A. & Hayashi, J.-I. A review on methane transformation to hydrogen and nanocarbon: Relevance of catalyst characteristics and experimental parameters on yield. Renew. Sustain. Energy Rev. 76, 743–767 (2017).
Li, Y., Li, D. & Wang, G. Methane decomposition to COx-free hydrogen and nano-carbon material on group 8–10 base metal catalysts: A review. Catal. Today 162(1), 1–48 (2011).
Awadallah, A., Aboul-Enein, A. & Aboul-Gheit, A. Effect of progressive Co loading on commercial Co–Mo/Al2O3 catalyst for natural gas decomposition to COx-free hydrogen production and carbon nanotubes. Energy Convers. Manag. 77, 143–151 (2014).
Rastegarpanah, A. et al. Influence of group VIB metals on activity of the Ni/MgO catalysts for methane decomposition. Appl. Catal. B Environ. 248, 515–525 (2019).
Saconsint, S. et al. Development of Ni-Mo carbide catalyst for production of syngas and CNTs by dry reforming of biogas. Sci. Rep. 13(1), 12928 (2023).
Yuan, Y., Huang, E., Hwang, S., Liu, P., Chen, J. G. Converting carbon dioxide into carbon nanotubes by reacting with ethane. Angewandte Chemie International Edition n/a (n/a), e202404047.
Rattanaamonkulchai, R. et al. Simultaneous production of hydrogen and carbon nanotubes from biogas: On the design of combined process. Int. J. Hydrogen Energy 47(32), 14432–14452 (2022).
Cao, A. N. T. et al. Insight into the role of material basicity in the coke formation and performance of Ni/Al2O3 catalyst for the simulated-biogas dry reforming. J. Energy Inst. 108, 101252 (2023).
Charisiou, N. D. et al. Investigating the correlation between deactivation and the carbon deposited on the surface of Ni/Al2O3 and Ni/La2O3-Al2O3 catalysts during the biogas reforming reaction. Appl. Surf. Sci. 474, 42–56 (2019).
Baena-Moreno, F. M. et al. Synergizing carbon capture storage and utilization in a biogas upgrading lab-scale plant based on calcium chloride: Influence of precipitation parameters. Sci. Total Environ. 670, 59–66 (2019).
Baena-Moreno, F. et al. Biogas upgrading by cryogenic techniques. Environ. Chem. Lett. 17, 1251–1261 (2019).
Kludpantanapan, T. et al. Development of CoMo-X catalysts for production of H2 and CNTs from biogas by integrative process. J. Environ. Chem. Eng. 10(4), 107901 (2022).
Angelidaki, I. et al. Biogas upgrading and utilization: Current status and perspectives. Biotechnol. Adv. 36(2), 452–466 (2018).
Awadallah, A. E., Aboul-Enein, A. A. & Aboul-Gheit, A. K. Impact of group VI metals addition to Co/MgO catalyst for non-oxidative decomposition of methane into COx-free hydrogen and carbon nanotubes. Fuel 129, 27–36 (2014).
Zhang, X. et al. High-performance binary Mo–Ni catalysts for efficient carbon removal during carbon dioxide reforming of methane. ACS Catal. 11(19), 12087–12095 (2021).
Patel, N., Al-Fatesh, A., Bamatraf, N., Osman, A., Alreshaidan, S., Fakeeha, A., Wazeer, I., Kumar, R. 5Ni/MgO and 5Ni/MgO + MOx (M = Zr, Ti, Al) catalyst for hydrogen production via dry reforming of methane: Promotor-free, cost-effective, and handy catalyst system. Catal. Lett. 1–16 (2024).
Peng, Z., Luo, X., Xie, Z. & Yang, M. Sintering behavior and mechanical properties of spark plasma sintering SiO2-MgO ceramics. Ceram. Int. 46(3), 2585–2591 (2020).
Rattanaamonkulchai, R. et al. Simultaneous production of hydrogen and carbon nanotubes from biogas over mono- and bimetallic catalyst. J. Environ. Chem. Eng. 10(4), 107910 (2022).
Li, W. Z., Wen, J. G. & Ren, Z. F. Effect of temperature on growth and structure of carbon nanotubes by chemical vapor deposition. Appl. Phys. A 74(3), 397–402 (2002).
Gao, Y., Jiang, J., Meng, Y., Yan, F. & Aihemaiti, A. A review of recent developments in hydrogen production via biogas dry reforming. Energy Convers. Manag. 171, 133–155 (2018).
Kharissova, O. V. & Kharisov, B. I. Variations of interlayer spacing in carbon nanotubes. RSC Adv. 4(58), 30807–30815 (2014).
Chai, S.-P., Seah, C.-M. & Mohamed, A. R. A parametric study of methane decomposition into carbon nanotubes over 8Co-2Mo/Al2O3 catalyst. J. Nat. Gas Chem. 20(1), 84–89 (2011).
Tan, W. H., Lee, S. L. & Chong, C. T. TEM and XRD analysis of carbon nanotubes synthesised from flame. Key Eng. Mater. 723, 470–475 (2017).
Ming, H., Peiling, D., Yunlong, Z., Jing, G. & Xiaoxue, R. Effect of reaction temperature on carbon yield and morphology of CNTs on copper loaded nickel nanoparticles. J. Nanomater. 2016, 8106845 (2016).
Garlow, J. A. et al. Large-area growth of turbostratic graphene on Ni(111) via physical vapor deposition. Sci. Rep. 6(1), 19804 (2016).
Awadallah, A. E., Aboul-Enein, A. A., El-Desouki, D. S. & Aboul-Gheit, A. K. Catalytic thermal decomposition of methane to COx-free hydrogen and carbon nanotubes over MgO supported bimetallic group VIII catalysts. Appl. Surf. Sci. 296, 100–107 (2014).
Serrano-Lotina, A. & Daza, L. Highly stable and active catalyst for hydrogen production from biogas. J. Power Sources 238, 81–86 (2013).
Pawar, V., Ray, D., Subrahmanyam, C. & Janardhanan, V. M. Study of short-term catalyst deactivation due to carbon deposition during biogas dry reforming on supported Ni catalyst. Energy Fuels 29(12), 8047–8052 (2015).
Kitiyanan, B., Alvarez, W. E., Harwell, J. H. & Resasco, D. E. Controlled production of single-wall carbon nanotubes by catalytic decomposition of CO on bimetallic Co–Mo catalysts. Chem. Phys. Lett. 317(3), 497–503 (2000).
Shi, Z. et al. Purification of single-wall carbon nanotubes. Solid State Commun. 112, 35–37 (1999).
Lehman, J. H., Terrones, M., Mansfield, E., Hurst, K. E. & Meunier, V. Evaluating the characteristics of multiwall carbon nanotubes. Carbon 49(8), 2581–2602 (2011).
Okonkwo, U. C., Onokpite, E. & Onokwai, A. O. Comparative study of the optimal ratio of biogas production from various organic wastes and weeds for digester/restarted digester. J. King Saud Univ. Eng. Sci. 30(2), 123–129 (2018).
Etim, U. J., Zhang, C. & Zhong, Z. Impacts of the catalyst structures on CO(2) activation on catalyst surfaces. Nanomaterials (Basel) 11(12), 3265 (2021).
Pujari, R. B., Lokhande, V. C., Kumbhar, V. S., Chodankar, N. R. & Lokhande, C. D. Hexagonal microrods architectured MoO3 thin film for supercapacitor application. J. Mater. Sci. Mater. Electron. 27(4), 3312–3317 (2016).
Brush, A., Evans, E. J., Mullen, G. M., Jarvis, K. & Mullins, C. B. Tunable Syn-gas ratio via bireforming over coke-resistant Ni/Mo2C catalyst. Fuel Process. Technol. 153, 111–120 (2016).
Simate, G. S., Iyuke, S., Ndlovu, S., Yah, C. & Walubita, L. The production of carbon nanotubes from carbon dioxide: Challenges and opportunities. J. Nat. Gas Chem. 19, 453–460 (2010).
Yan, X.-L. et al. Melamine as a single source for fabrication of mesoscopic 3D composites of N-doped carbon nanotubes on graphene. RSC Adv. 8(22), 12157–12164 (2018).
Karthikeyan, S. & Mahalingam, P. Carbon nanotubes from unconventional resources: Part A: Entangled multi-walled carbon nanotubes and Part B: Vertically-aligned carbon nanotubes. In Syntheses and Applications of Carbon Nanotubes and Their Composites (ed. Satoru, S.) 11 (IntechOpen, 2013).
Venkatesan, S., Visvalingam, B., Mannathusamy, G., Viswanathan, V. & Rao, A. G. Effect of chemical vapor deposition parameters on the diameter of multi-walled carbon nanotubes. Int. Nano Lett. 8(4), 297–308 (2018).
Kara, M. H., Teh, A. A., Ahmad, R., Rusop, M. & Awang, Z. In Gas flow rate and synthesis time dependence of MWCNT growth by chemical vapour deposition, 2011 IEEE International RF & Microwave Conference, 12–14 Dec. 2011; 2011; pp 359–362.
Acknowledgements
This research project is supported by Mahidol University (Fundamental Fund: fiscal year 2023 by National Science Research and Innovation Fund (NSRF)). Authors also would like to thank Nawapol Udpuay, Chawalit Takoon, Suwilai Chaveanghong, and Bancha Panyacharoen scientists at Mahidol University—Frontier Research Facility (MU-FRF) for their kind assistance in instrumental operation of XRD and Raman spectroscopy.
Author information
Authors and Affiliations
Contributions
N.S.: Conceptualization, Investigation, Methodology, Data curation, and Writing- Original draft preparation. S.S.: Investigation, Methodology, Data curation, and Writing- Original draft preparation. A.S.: Resources, Visualization, and Validation. W.K.-A.: Resources. S.A.: Resources, Visualization, and Validation. C.F.: Resources, and Visualization. S.R.: Conceptualization, Methodology, Validation, Visualization, Data curation, Supervision, Funding acquisition, and Writing-Reviewing and Editing.
Corresponding author
Ethics declarations
Competing interests
The authors declare no competing interests.
Additional information
Publisher's note
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Rights and permissions
Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons licence, and indicate if changes were made. The images or other third party material in this article are included in the article's Creative Commons licence, unless indicated otherwise in a credit line to the material. If material is not included in the article's Creative Commons licence and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this licence, visit http://creativecommons.org/licenses/by/4.0/.
About this article
Cite this article
Sae-tang, N., Saconsint, S., Srifa, A. et al. Simultaneous production of syngas and carbon nanotubes from CO2/CH4 mixture over high-performance NiMo/MgO catalyst. Sci Rep 14, 16282 (2024). https://doi.org/10.1038/s41598-024-66938-6
Received:
Accepted:
Published:
DOI: https://doi.org/10.1038/s41598-024-66938-6
- Springer Nature Limited