Impact of operating parameters on CO2 capture using carbon monolith by Electrical Swing Adsorption technology (ESA)
Introduction
Carbon dioxide (CO2), a major greenhouse gas, is emitted from a range of industries such as power plants, iron and steel, refining, petrochemical, and cement manufacturing. If the emission trend continues, the average global temperature will increase by around 6 °C in the long term [8], [9].
Carbon capture and storage CCS) is one potential technology to help mitigate these Greenhouse Gas GHGs) emissions [12]. There are at least five technologies which have been explored for post-combustion CO2 capture – solvent absorption, solid adsorption, cryogenics technology, membrane separation, and microbial/algal systems [13], [19]. Solvent absorption, solid adsorption, and membrane technology are the most mature technologies for CO2 capture, with solvent absorption currently deployed in capture plants at Boundary Dam and Petra Nova. Although solvent absorption is readily scaled up, it has a high energy demand for regeneration and also poses problems such as solvent loss by evaporation, equipment corrosion and formation of potentially carcinogenic nitrosamines [11]. Compared with absorption, adsorption-based technology offers a number of advantages such as simplicity of operation, relatively low energy requirement and ease of retrofitting to existing facilities [20]. This technology, which has been developed over the past decades, includes Pressure Swing Adsorption (PSA), Vacuum Swing Adsorption (VSA), Temperature Swing Adsorption (TSA) and Electrical Swing Adsorption (ESA). ESA has recently attracted interest because it can quickly and directly heat the adsorbent for regeneration via the Joule effect, resulting in a short heating time and high regeneration efficiency [18]. Thus, higher gas throughput, high purity and recovery can be achieved by ESA, compared to conventional TSA in which gases are used to heat the bed.
The adsorbent in ESA must also be electrically conducting, so activated carbon in a continuous form such as a monolith) is a common adsorbent for this technology [18]. Compared with activated carbon beads and fiber cloth, activated carbon in monolith form is preferred in the ESA process [10], due to its lower pressure drop, higher permeability, higher electrical resistivity and lower cost. Yu et al. [24] first proposed electrothermal desorption on an activated carbon monolith using the Joule effect. They controlled the desorption rate by maintaining electrical current and a specific purge gas flow rate in removal of toluene. Subsequently, they conducted a series of experiments and theoretical simulations on the removal of toluene by the ESA process using activated carbon monolith and found that the maximal desorbed concentration of toluene and recovery increased almost linearly with current intensity and purge flow rate [23]. In 2008, Grande et al., simulated CO2 removal from a mixture of low concentrated CO2 balanced with Helium. From their simulation, a CO2 purity of 16% with a recovery of 89% was obtained using a feed gas with 4.5% CO2 at an adsorption temperature of 293 K and desorption temperature of 423 K [6]. They studied the effect of electrode materials on electrothermal performance and found brass electrodes presented lower energy losses in the contact between the electrode and the surface of monolith [16]. They also designed a novel ESA processing cycle with seven steps including feed, rinse with recycled gas, internal rinse, electrification, depressurization and purge to separate CO2 from a mixture of low concentrated CO2 balanced with N2. A CO2 purity of 89.8% with a recovery of 72.0% was achieved from their simulation [4]. Furthermore, in order to improve adsorption characteristics of activated carbon monolith on CO2, a hybrid zeolite 13X monolith system was employed, CO2 product with purity of 46.6% and recovery of 80% was obtained experimentally from the six step ESA cycle and the estimated energy consumption could be reduced to 6 GJ/tonne CO2 [17].
Research on CO2 capture from flue gases by ESA technology is still in its infancy. It is important therefore to systematically investigate the influence of ESA operating parameters on ESA performance, specifically CO2 purity, recovery and energy efficiency. The major variables affecting these performance metrics are electrification time, current intensity, and nitrogen purge. In this study, a four–step ESA cycle was used, and included adsorption, electrification, N2 purge and cooling steps. In order to reduce the amount of experiments, a central composite design (CCD) was employed to analytically design a series of experiments with various parameters [7] using the Design Expert Design of Experiments software. In this software package, response surface methodology (RSM) [2], [3], [14], was applied to analyse the experimental data and to determine how important these factors (current intensity, electrification time and purge rate) were in affecting CO2 purity, recovery, CO2 harvest time and energy consumption. Furthermore, optimal values of the operating parameters, such as electric current, electrification time, N2 purge rate and time for CO2 capture process, at fixed electric current, were determined and confirmed by experimental data and simulation results.
Section snippets
Activated carbon monolith
An activated carbon monolith from MAST© Carbon (UK) was employed in this project. The physical properties are provided in Table 1.
Isotherms of CO2 and N2 on this monolith were measured with a gas sorption analyser (ASAP2010, Micrometritics, US) at temperatures of 293.15 K, 323.15 K and 373.15 K, and are shown in Fig. 1. Single site Langmuir parameters fitted from the experimental data are provided in Table 2.
ESA apparatus
As shown in Fig. 2, the ESA rig contains three parts: gas delivery system, adsorption
Theoretical work
To help explain our observations and to extend the range of predictions, we developed a simulation model for the ESA process. In order to simplify model complexity and reduce computation time, every channel in the monolith was assumed to have identical geometry and condition. Thus, the behaviour in one channel can represent those in the overall monolith [22]. The one channel model is further simplified to 1D.
Mass balance of component i in the gas phase in a monolith channel is shown in Eq. (1):
Determination of linear driving force coefficient
The kinetic coefficient (kLDF) for the linear driving force (LDF) model was obtained by matching breakthrough data to the simulation as shown in Fig. 3.
The simulation result with kLDF = 0.1 was in a good agreement with experimental data, and then this kinetic coefficient was further verified in the following desorption step.
In this experiment, a constant current of 12 A was employed to heat the monolith with which the breakthrough experiment had just been conducted. After 100 s electrification, N2
Conclusion and future work
In this study, a simple 4-step ESA experiment was employed to investigate how Joule heat and N2 purge rate affect the CO2 recovery, product purity and harvest time in an electric swing adsorption process using a commercial carbon monolith. A simplified theoretical model was also validated by a series of adsorption breakthrough and desorption experiments.
By analysing the experimental data of different electric current, N2 purge rates and electrification time, current and electrification time had
Acknowledgements
We acknowledge the financial support of The University of Melbourne as well as the funding provided by Brown Coal Innovation Australia. We acknowledge useful discussions with partners in the European Commission Framework 7 MATESA project.
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