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1876-6102 © 2017 The Authors. Published by Elsevier Ltd. This is an open access article under the CC BY-NC-ND license (http://creativecommons.org/licenses/by-nc-nd/4.0/).

Peer-review under responsibility of the scientific committee of the 8th International Conference on Applied Energy. doi: 10.1016/j.egypro.2017.03.576

Energy Procedia 105 ( 2017 ) 2016 – 2021

ScienceDirect

The 8

th

International Conference on Applied Energy – ICAE2016

The effect of temperature and initial methane concentration

on carbon dioxide methanation on Ni based catalysts

Kristian Stangeland

1

, Dori Kalai

1

, Hailong Li

2

, Zhixin Yu

1

*

1Department of Petroleum Engineering, University of Stavanger, 4036 Stavanger, Norway 2Department of Energy, Building and Environment, Mälardalen University, 73123 Västerås, Sweden

Abstract

A series of Ni based catalysts prepared by incipient wetness method were characterized by chemisorption and studied for CO2 methanation. Ru had apparently a positive effect on the active metal surface area, and thus the catalytic activity. The CO2 conversion was greatly affected by temperature where the conversion ranged from 12%-85% at temperatures of 300 to 400 oC on the 12% Ni/Al2O3 catalyst. At 350 oC, higher Ni loading resulted in increased activity. The incorporation of 0.5% Ru lead to a drastic increase in catalytic activity, which can be explained by increased reducibility and a synergetic effect between Ni and Ru, and was further enhanced by increased Ni loading. Addition of CH4 at twice the initial concentration of CO2 to the feed gas mixture was found to decrease the conversion from 52% to 48% at 350 oC on the 20% Ni/Al2O3 catalyst, whereas only a slight reduction in selectivity was observed. The results preliminary demonstrate that high methane purity can be achieved from a biogas feed stream over Ni based catalysts.

© 2016 The Authors. Published by Elsevier Ltd.

Selection and/or peer-review under responsibility of ICAE

Keywords: CO2 Methanation; Nickel; Ruthenium; Biogas Upgrading

1. Introduction

The CO2 concentration is continuously increasing in the atmosphere, which is considered to be one of

the anthropogenic causes of global warming, and has led to growing interest in CO2 capture, utilization and

storage (CCUS). CO2 is an attractive C1 building block for making fuels, chemicals, materials and

carbohydrates (i.e., foods). CO2 methanation is being considered for intermittent renewable energy storage

in power-to-gas technology [1]. Additionally, investigations of its potential as a biogas upgrading technique are being carried out. Biogas contains a significant amount of CO2 in addition to CH4. Thermodynamic

* Corresponding author. Tel.: +47-5183-2238; fax: +47-5183-2050

E-mail address: zhixin.yu@uis.no

© 2017 The Authors. Published by Elsevier Ltd. This is an open access article under the CC BY-NC-ND license (http://creativecommons.org/licenses/by-nc-nd/4.0/).

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simulations predict that the initial CH4 concentration will have a low impact on the conversion of CO2 and

the CH4 selectivity, particularly at elevated pressures [2].

Methanation of CO2, or the so-called Sabatier reaction, is an exothermic reaction in which H2 and CO2

react to form CH4 and H2O. The reaction stoichiometry is as shown in equation 1. The most widely accepted

mechanism for this reaction is first stripping of an oxygen atom from CO2 to form CO, followed by CO

methanation.

CO2 + 4H2 → CH4 + 2H2O ∆H = -165 kJ/mol (1)

Ni based catalyst has been extensively studied for the CO2 methanation reaction, typically on high

surface area supports (i.e., Al2O3, SiO2, ZrO2, TiO2, CeO2) [3]. However, Ni based catalyst often suffers

from low conversions at low temperatures and is subject to sintering and coke deposition at high temperatures [4]. Recently, great interest has been shown on hydrotalcite-derived Ni catalyst, and promoters such as La [5] and Fe [6] have been demonstrated to improve the reaction rates over such catalysts. Garbarino et al. [7] compared a commercial 3% Ru/Al2O3 to a commercial 20% Ni/Al2O3 catalyst and

found that the Ru based catalyst performed equally or better than the Ni based catalyst depending on the reaction conditions.

In the present study, a series of 12 and 20% Ni catalysts, either unpromoted or promoted by 0.5% Ru, have been investigated for the CO2 methanation reaction for biogas upgrading. The effect of temperature is

firstly investigated on a 12% Ni/Al2O3 catalyst for CO2 methanation. The influence of Ni loading and Ni

modification with 0.5% Ru on the catalysts’ activity and selectivity is also reported. Additionally, the selected 20% Ni/Al2O3 catalyst was subjected to a biogas feed stream of CH4/CO2, and compared with a

pure feed of CO2 to study the effect of CH4 on CO2 methanation.

2. Experimental

2.1. Catalyst preparation

All catalysts were prepared by the incipient wetness impregnation method. The γ-Al2O3 (SCCa 5-200,

from Sasol Germany) support was calcined in flowing air at 600 oC prior to impregnation. Ni(NO

3)2∙6H2O

and Ru(NO)(NO3)2∙xH2O precursors purchased from Sigma-Aldrich were used. For the monometallic Ni

catalysts, a calculated amount of the aqueous solution of Ni salt was added to the support material to achieve the desired loading. Bimetallic catalysts were prepared by co-impregnation where the support was impregnated by the aqueous solution mixture of Ni and Ru salts. The catalyst was dried at 120 oC for 24 h,

followed by calcination in flowing air, where the temperature was increased from room temperature to 600

oC at a ramp rate of 10 oC/min, and maintained at 600 oC for 6 h. The prepared catalysts are as listed in

Table 1.

2.2. Chemisorption study of the catalysts

The active metal surface area and metal dispersion were measured by a volumetric chemisorption apparatus (ASAP 2020 Plus, Micromeritics). The sample was placed in a quartz u-tube and held by a quartz wool plug. 300 mg catalyst was used for each measurement. First, the sample was pretreated to dry the sample in He flow while the temperature was ramped from ambient to 200 oC at a rate of 25 oC/min. Then

the sample was heated to 600 oC at 10 oC/min in flowing H

2. After reducing the catalyst for 30 min at 600 oC, the sample was cooled to 35 oC at a rate of 10 oC/min in vacuum. Next, the H

2 adsorption was recorded

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2.3. CO2 methanation activity test

The experiment for CO2 methanation was performed in a fixed bed tubular reactor with an internal

diameter of 12.7 mm at atmospheric pressure. A schematic of the home-built reactor is shown in Fig. 1. A thermocouple was installed on top of the catalyst bed to measure the temperature. The mixture of 150 mg catalyst with 1500 mg γ-Al2O3 was placed on top of an internal stainless steel tube with 9 mm internal

diameter, and a quartz wool plug held the mixture in place. The catalyst was reduced at 600 oC for 6 h

before the reaction. After cooling to the reaction temperature in N2, the feed gas with the desired H2, CO2,

N2 and CH4 concentration was introduced into the reactor, where the H2/CO2 ratio of 4 was fixed.

Concentration of the effluent gases from the reactor was determined by an online GC (Agilent 7890B) equipped with a thermal conductivity detector.

Fig. 1: Schematic of the catalytic activity test setup for CO2 methanation.

3. Results and discussion

3.1. Chemisorption study

The results of the chemisorption characterization are presented in Table 1. Modification with Ru had a clear effect and improved the active metal area. As can been seen the addition of Ru was particularly effective for the 20Ni0.5Ru/Al2O3 catalyst, which has a significantly higher metal surface area than the

20Ni/Al2O3 catalyst. This can be attributed to a large reduction degree when Ru is present, which increased

the effective Ni metallic surface area significantly.

Table 1. Prepared catalysts and chemisorption results

Catalyst Denotation Ni (wt.%) Ru (wt.%) Total Quantity H2 adsorbed (cm3/g

cat STP)

Active metal area (m2/g cat) 12Ni/Al2O3 12 0 1.989 3.92 12Ni0.5Ru/Al2O3 12 0.5 2.170 4.15 20Ni/Al2O3 20Ni0.5Ru/Al2O3 20 20 0 0.5 1.817 2.358 3.30 4.39

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3.2. Activity tests at different temperatures and catalyst stability

In Fig.2 (a) the CO2 conversion and the CH4 selectivity at different temperatures on the 12Ni/Al2O3

catalyst are reported. The achieved conversions of 12%-85% from 300 to 400 oC are below the equilibrium

predicted by thermodynamics, which can be attributed to the high gas hourly space velocity (GHSV) at 40,000 mL (gcat h)-1 used in our experiments. The rapid decrease in conversion at lower temperatures shows

that under the investigated temperature range of 300-400 oC, the methanation reaction is kinetically

controlled on the 12Ni/Al2O3 catalyst. The CH4 selectivity was found to only change slightly with

temperature, even though thermodynamics predicts improved selectivity at lower temperatures [7]. To investigate the stability of the prepared catalysts, an experiment was run at 400 oC on the 12Ni/Al

2O3

catalyst for 36 h time on stream (TOS), and the result is presented in Fig. 2 (b). It is evident that the catalyst was not subjected to deactivation, meaning sintering and carbon deposition did not occur. The calcination temperature could explain the absence of sintering, as the resulting Ni particles are more stable at higher calcination temperatures. As expected, the selectivity remained constant at 99% throughout TOS.

Fig. 2. (a) CO2 conversion and CH4 selectivity at 300, 350 and 400 oC with GHSV of 40,000 mL (gcat h)-1; and (b) long term stability test at 400 oC. All experiments were conducted on the 12Ni/Al

2O3 catalyst at flowrate of 100 mL/min with a H2/CO2 ratio of 4.

3.3. Activity of different catalysts

The activity of the different catalysts for CO2 methanation were tested at a fixed temperature of 350 oC.

The CO2 conversion and the CH4 selectivity over different Ni based catalysts are plotted in Fig. 3 (a) and

(b) respectively. The highest conversion of 75% was obtained over the 20Ni0.5Ru/Al2O3 catalyst, which is

much higher than the 55% achieved over the 12Ni0.5Ru/Al2O3. Interestingly, the 12Ni0.5Ru/Al2O3 catalyst

has 3% higher conversion than the 20Ni/Al2O3, while the 20Ni/Al2O3 has 12% higher conversion than the

12Ni/Al2O3 one. In addition, the higher activity of the 20Ni0.5Ru/Al2O3 catalyst cannot be explained by

the Ni loading alone. It shows that there is potentially a synergistic effect between Ni and Ru, which has contributed to the high activity of the Ru containing catalysts. This is not surprising as Ru has been shown to have superior activity at lower temperatures [7]. Thus, the results demonstrate that small amounts of Ru can significantly improve the reaction rate at relatively low temperatures for Ni based catalysts.

The catalyst activity was found to be stable after 14 h TOS for all catalysts. Likewise, the selectivity remained constant. CH4 selectivity was close to 99% for all catalyst, where both the addition of Ru and the

increased Ni loading had a positive effect. The 20Ni0.5Ru/Al2O3 catalyst showed a marked increase in CH4

selectivity of 99.6% whereas 12Ni0.5Ru/Al2O3 and 12Ni/Al2O3 had a selectivity of 98.8% and 99.7%

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Fig. 3. (a) CO2 conversion and (b) CH4 selectivity of different catalysts at 350 oC. Total flowrate is 140 mL/min with a GHSV 56,000 mL (gcat h)-1 and a reactant ratio of H2:CO2:N2 4:1:2.

3.4. Effect of initial CH4 concentration

The effect of initial CH4 concentration was studied at 350 oC with the selected 20Ni/Al2O3 catalyst,

which is closer to the nickel loading of a normal commercial catalyst. In Fig. 4 a comparison of CO2

conversion (a) and CH4 selectivity (b) with and without initial CH4 concentration in the feed is presented.

N2 was added when CH4 was absent to maintain the same GHSV as well as the partial pressures of CO2

and H2. When CH4 is added twice the concentration of CO2, a decrease of 4% in CO2 conversion and 0.2%

in CH4 selectivity was observed. This is expected according to le Chatelier’s principle, as CH4 is one of the

products of CO2 methanation. It is also in accordance with the simulations by Jürgensen et al. [2], who

showed that initial CH4 concentration will decrease the CO2 conversion and the CH4 selectivity slightly at

atmospheric pressure. The results confirm that high CO2 conversion and CH4 selectivity can be achieved

from a biogas containing CH4 and CO2 by our 20Ni/Al2O3 catalyst prepared by incipient wetness.

The presence of initial CH4 was proposed to potentially result in increased carbon deposition at

temperatures above 316 oC and atmospheric pressure [7]. However, the catalyst remained stable during

TOS of 14 h, which shows that the 20Ni/Al2O3 catalyst is rather stable at the reaction conditions.

Fig. 4. The effect of initial CH4 on (a) CO2 conversion and (b) CH4 selectivity. The total flowrate is 140 mL at GHSV 56,000 mL(gcat h)-1, and CH4 is added twice the concentration of CO2.

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4. Conclusion

In this study, it has been shown that the activity of the Ni based catalyst depends greatly on the reaction temperature where the CO2 conversion ranged from 12%-85% at temperatures of 300 to 400 oC. However,

the catalyst displayed great stability and remained very stable after 36 h time on stream at the high reaction temperature of 400 oC.

Comparison of the prepared catalysts confirmed that Ru increased the activity of the Ni based catalyst significantly, as well as improved the selectivity of CH4. The increase of the activity could be explained by

the improved reducibility of Ni and the synergistic effect between Ni and Ru. Increased Ni loading was also beneficial for activity and selectivity. The highest conversion of 75% and selectivity of 99.6% was obtained for the 20Ni0.5Ru/Al2O3 catalyst at 350 oC.

When CH4 is added twice the initial concentration of CO2 in the feed gas mixture, the CO2 conversion

decreased slightly from 52% to 48% on the 20Ni/Al2O3 catalyst at 350 oC. Only a slight reduction in

selectivity was observed. The results demonstrate that high purity CH4 can be achieved from a biogas feed

stream over our Ni catalysts. Acknowledgements

The authors would like to thank the financial support from Department of Petroleum Engineering, University of Stavanger for this project.

References

[1] Götz M, Lefebvre J, Mörs F, Koch AM, Graf F, Bajohr S, Reimert R, Kolb T. Renewable Power-to-Gas: A technological and economic review. Renew Energ 2016;85:1371-1390.

[2] Jürgensen L, Ehimen EA, Born J, Holm-Nielsen JB. Dynamic biogas upgrading based on the Sabatier process: thermodynamic and dynamic process simulation. Bioresource Technol 2015;178:323-329.

[3] Wei W, Jinglong G. Methanation of carbon dioxide: an overview. Front chem sci eng 2011;5:2-10.

[4] Ma S, Tan Y, Han Y. Methanation of syngas over coral reef-like Ni/Al2O3 catalysts. J of Natural Gas Chem 2011;20:435-440.

[5] Wierzbicki D, Debek R, Motak M, Grzybek T, Gálves ME, Da Costa P. Novel Ni-La hydrotalcite dericed catalysts for CO2 methanation. Catal Commun 2016;83:5-8.

[6] Wang X, Zhen T, Yu C. Applications of Ni-Al-hydrotalcite-derived catalyst modified with Fe or Mg in CO2 methanation.

Appl Petrochem Res 2016;6:1-7.

[7] Garbarino G, Bellotti D, Riani P, Magistri L, Busca G. Methanation of carbon dioxide on Ru/Al2O3 and Ni/Al2O3 catalysts at atmospheric pressure: Catalyst activation, behaviour and stability. Int J of Hydrogen Energ 2015;40:9171-9182.

Biography

Zhixin Yu is Professor at Department of Petroleum Engineering, University of Stavanger, Norway. He received his doctorate in Chemical Engineering from Norwegian University of Science and Technology (2005). He has then worked as research scientist at SINTEF, IRIS and Statoil. His main research interests are energy production by nanotechnology.

Figure

Fig. 1: Schematic of the catalytic activity test setup for CO 2  methanation.
Fig. 2. (a) CO 2  conversion and CH 4  selectivity at 300, 350 and 400  o C with GHSV of 40,000 mL (g cat  h) -1 ; and (b) long term stability  test at 400  o C
Fig. 4. The effect of initial CH 4  on (a) CO 2  conversion and (b) CH 4  selectivity

References

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