Membrane contactors modelled for process intensification post combustion solvent regeneration
Introduction
Membrane gas solvent contactors for CO2 capture in a post-combustion scenario are able to combine the high selectivity for CO2 of a solvent absorption process within the compact module of a membrane (Simons et al., 2009; Zhao et al., 2016). This is achieved by having a semi-permeable membrane separating the solvent and gas phases, and hence the mass transfer area per unit volume is significantly higher than a traditional solvent column. Furthermore, the two phases’ flows are strictly controlled within the membrane module to avoid flooding and entrainment. These advantages have made membrane contactors attractive alternatives to traditional solvent absorption processes, with a number of pilot plants trialled (Scholes et al., 2014, 2012). The majority of membrane contactor research for CO2 capture has focused on the absorption process using both porous and non-porous membranes with various solvents (Kosaraju et al., 2005; Scholes et al., 2015a). Importantly, this research has demonstrated that membrane contactors’ can reduce the volume of the equipment needed to undertake CO2 absorption compared to traditional solvent columns, known as process intensification (Falk-Pedersen and Dannstrom, 1997; Favre and Svendsen, 2012; Mendez et al., 2017; Nguyen et al., 2011). This is important in many carbon capture situations where space is limited, such as off-shore platforms. Regeneration of the CO2 loaded solvent (i.e. stripping) through a membrane contactor is less reported in the literature, though a number of recent studies have demonstrated the feasibility (Dibrov et al., 2014; Khaisri et al., 2011; Koonaphapdeelert et al., 2009; Simioni et al., 2011). The major advantage of membrane contactors in solvent regeneration is the ability to remove the CO2 from the solvent below the vaporization temperature of the loaded solvent. This can be achieved through either the gas phase being under vacuum or applying a sweep gas, generally steam. This enables the CO2 partial pressure above the solvent to be reduced below the vapour-liquid equilibrium, resulting in CO2 liberation from the solvent, and hence CO2 desorption without full vaporization of the solvent. Critically, for membrane contactors undertaking solvent regeneration, a full scale process has not been studied or modelled to date to determine the viability of replacing a traditional desorber column with a membrane contactor. This is addressed in this investigation by modelling a large scale membrane contactor process for solvent regeneration and comparing the relative performance to a traditional solvent desorber column in terms of module length, process volume and therefore process intensification, as well as energy duty.
A number of reliable mass and energy transfer models have been developed for membrane contactors undertaking CO2 absorption. Here, two models are presented and utilised for CO2 desorption from a solvent; a simple mass transfer approximation adapted from packed columns and a more detailed one-dimensional model for mass transfer through hollow fibers. The contactors modelled are based on a non-porous composite membranes consisting of Teflon AF1600 on porous polypropylene (PP) and an asymmetric polydimethylsiloxane (PDMS), given that their performance in the literature has previously been reported for solvent regeneration over a range of temperatures (Scholes et al., 2016, 2015b). The loaded solvent undergoing regeneration is 30 wt% monoethanolamine (MEA), given it is the generic standard for CO2 capture and the properties of the loaded and non-loaded solvent are well known. The evaluated modelled performance of these two contactors will provide insight into the viability of membrane contactors to achieve process intensification for CO2 desorption.
Section snippets
Theory
For the desorption of CO2 through a membrane contactor, the molar flux (N (mol/m2 s)) is given by (Boucif et al., 2012):where KOL (ms−1) the overall liquid phase mass transfer coefficient and ΔCLM represents the log mean average of the concentration driving force (mol/m3) between the solvent and gas phases. The overall mass transfer across a non-porous membrane consists of four mass transfer steps, the transfer of CO2 across the solvent boundary layer, the transfer of CO2 through the
Contactor module length
The calculated length of the respective membrane modules to regenerate the loaded solvent is provided in Fig. 2, as a function of inlet solvent temperature and simulation model. The two models have comparable trends of decreasing contactor length with increasing inlet temperature. The longest contactor lengths occur for low inlet temperatures because of the corresponding low equilibrium vapour CO2 partial pressure at those temperatures. This resulted in a reduced driving force for mass
Conclusion
The simulation of two membrane contactors based on Teflon AF1600 and PDMS for the desorption of CO2 from 30 wt% MEA solvent has demonstrated that this approach has advantages in terms of process intensification and energy duty compared to traditional desorber column. Two models to simulate a membrane contactor undergoing desorption were investigated, a simple approximation model and a more rigorous one-dimensional model. Both models have the same trend with temperature, of a reduction in
References (31)
- et al.
CO2 capture from power plants. Part 1. A parametric study of the technical performance based on monoethanolamine
Int. J. Greehouse Gas Control
(2007) - et al.
Stripping of CO2 in post-combustion capture with chemical solvents: intensification potential of hollow fiber membrane contactors
Energy Procedia
(2017) - et al.
Simulation of CO2 capture using MEA scrubbing: a flowsheet decomposition method
Energy Conv. Management
(2005) - et al.
Robust high-permeance PTMSP composite membranes for CO2 membrane gas desorption at elevated temperatures and pressures
J. Membr. Sci.
(2014) - et al.
Separation of carbon dioxide from offshore gas turbine exhaust
Energy Conv. Manag.
(1997) - et al.
CO2 chemical absorption by using membrane vacuum regenreation technology
Energy Procedia
(2009) - et al.
Membrane contactors for intensified post-combustion carbon dioxide capture by gas-liquid absorption processes
J. Membr. Sci.
(2012) - et al.
Absorption and regeneration performance of novel reactive amine solvents for post-combustion CO2 capture
Energy Procedia
(2011) - et al.
CO2 stripping from monoethanolamine using a membrane contactor
J. Membr. Sci.
(2011) - et al.
Carbon dioxide stripping in ceramic hollow fibre membrane contactors
Chem. Eng. Sci.
(2009)
A dense membrane contactor for intensified CO2 gas/liquid absorption in post-combustion capture
J. Membr. Sci.
Comparison of non-porous and porous membrane contactors for CO2 absorption into monoethanolamine
Int. J. Greenhouse Gas Control
Asymmetric composite PDMS membrane contactors for desorption of CO2 from monoethanolamine
Int. J. Greehouse Gas Control
Thin-film composite membrane contactors for desorption of CO2 from monoethanolamine at elevated temperature
Sep. Purif. Technol.
Membrane gas-solvent contactor trails of CO2 absorption from syngas
Chem. Eng. J.
Cited by (9)
Perspectives on the process intensification of CO<inf>2</inf> capture and utilization
2022, Chemical Engineering and Processing - Process IntensificationHolistic review on the recent development in mathematical modelling and process simulation of hollow fiber membrane contactor for gas separation process
2021, Journal of Industrial and Engineering ChemistryCitation Excerpt :On the gas boundary layer and liquid boundary layer, the concentration of gas varies along the radial direction due to the diffusion of gas components from the gas phase into the membrane and finally into the liquid phase. Typically, many assumptions have to be made in developing the 1D mathematical model [5,15–17]. These include steady state in gas and liquid phase, isothermal conditions throughout the HFMC module, laminar fluid flow, non-wetted/wetted mode in membrane, ideal gas behaviors, plug flow (non-uniform flow distribution due to random packing neglected), no axial dispersion, equilibrium at G-L interface according to the Henry’s law, Fick diffusion through the membrane, no convective contribution in shell and tube side, constant membrane mass transfer coefficient, concentration gradient is only considered in axial direction, uniform membrane pore distribution, no pressure drop along the fiber length, negligible pressure drop in liquid phase and no axial mixing in phases.
Mass transfer basics and models of membranes containing nanofluids
2021, Nanofluids and Mass TransferMembrane gas-solvent contactor pilot plant trials for post-combustion CO<inf>2</inf> capture
2020, Separation and Purification TechnologyCitation Excerpt :Membrane contactor technology is also able to replace the solvent regeneration stage, commonly known as stripping [7–9]. This is partially achieved by using steam as a sweep gas on the permeate side of the membrane contactor under vacuum conditions [10]. The reduced partial pressure on that side of the membrane draws CO2 from the solvent, enabling separation to occur without a solvent phase change, and hence achieve regeneration conditions at a lower temperature than conventional desorbers.