CO2 removal using 1DMA2P solvent via membrane technology: Rate based modeling and sensitivity analysis
Graphical Abstract
Introduction
Extensive efforts have been performed to solve environmental problems related to climate change and global warming [1], [2], [3]. The world is imposed to upgrade environmental strategies and applied efficient technologies that will reduce the greenhouse gas emissions into the atmosphere [4]. One of the main concerns for the future decades is mitigation of CO2 emissions as the largest contributor to greenhouse pollution. Post–combustion CO2 capture via chemical absorption process is a favorable method for carbon capture and storage (CCS). Amine solvents are usually used for this process since they represent high capture efficiency and selectivity towards CO2, low energy requirement for regeneration, low degradation rate, and low corrosiveness. Different amine–based solvents have been widely used for CO2 capture. Alkanolamine solvents can be categorized into three main groups, including primary, secondary and tertiary amines. Although, because of faster reaction rates of primary and secondary amines with CO2, they are extensively used, but also their use has been recently limited because of their low CO2 absorption capacity, solvent degradation and corrosion, high regeneration energy and cost. On the other hand, the tertiary amines represent higher absorption capacity, lower regeneration heat, as well as slower reaction rate. The tertiary amines catalyze the hydrolysis of CO2 to bicarbonate without any direct reaction with CO2. The superiority of lower energy consumption during regeneration of tertiary amines can provide the wide–spread employment of amine solvents. In recent years, the development of more efficient tertiary amine solvents has attracted extensive attention in the research community to provide a cost effective system. Currently, 1–dimethylamino–2–propanol (1DMA2P), a tertiary alkanolamine, introduced as an applicable solvent for large-scale use in bulk CO2 absorption. The previous investigations confirmed that 1DMA2P represents better mass transfer performance and higher kinetics of CO2 removal than the most common tertiary amines [5]. Liang et al. [5] investigated the CO2 removal performance of aqueous 1DMA2P in terms of CO2 absorption rate, CO2 absorption heat, CO2 equilibrium solubility, and mass transfer efficiency. Their reported results indicated that the equilibrium solubility of 1DAM2P solvent is greater than that of conventional amines such as MEA and MDEA. Kadiwala et al. [6] reported that 1DMA2P represents faster kinetics of CO2 absorption compared to that of MDEA. Afkhamipour et al. [7] experimentally and theoretically calculated the physical properties of 1DMA2P solution such as CO2 equilibrium solubility, density and viscosity. Liu et al. [8] determined the CO2 solubility and absorption heat into 1DMA2P. They inferred that the CO2 equilibrium solubility into 1DMA2P solution reduces as both reaction temperature and solvent concentration increases, and the CO2 solubility enhances as the CO2 partial pressure increases.
Gas-liquid absorption process is conventionally performed using sprayer, bubble, plated and packed columns, but the main challenge in designing and operating these columns is to intensify the mass transfer rate by providing as much contact area as possible. Another important drawback of these columns is the interdependence of the two fluid phases to be directly contacted, which may lead to problems such as foaming, flooding, emulsions and unloading. An alternative approach to overcome these disadvantages and provide substantially more contact area than conventional methods is non–dispersive contact via a membrane. Recently, hollow fiber membrane contactors (HFMC) are introduced as one of the most promising alternative to intensify the CO2 removal by chemical absorption. The main advantage of HFMC is to make use of permeable membrane to enhance chemical absorption with equilibrium–limited chemical reactions. Also, since two fluid streams are independent in the HFMC, the available contact area remains unchanged at various flow rates. Indeed, the membrane acts as a physical barrier and allows non–dispersive gas–liquid contact. Moreover, membrane contactors present flexibility, modularity, compact size, high contact area, easy installation and low cost.
HFMC has been extensively considered both theoretically and experimentally, and interesting results have been achieved in terms of CO2 removal from the flue gases. Cao et al. [9] studied the CO2 removal by aqueous 1DMA2P solution in a polytetrafluoroethene HFMC. Their reported results indicated that the enhancement of amine temperature and concentration will improve the CO2 removal efficiency. Experimental investigation by deMontigny et al. [10] showed that the overall mass transfer coefficient (KGav) in membrane contactor is significantly greater than that in the packed tower. Rangwala [11] studied and compared the CO2 absorption into different solvent via traditional packed column and membrane module. They observed that the KGav in HFMC can be 3–9 times greater than traditional packed column. Iliuta et al. [12] concluded that under the same specific surface area and volume, the HFMCs has a higher CO2 removal efficiency to the packed column. Also, they inferred that the CO2 absorption can be significantly intensified with an enhancement in the specific area of membrane module. More detailed literature review is presented by Saidi et al. [13,14], Luis et al. [15], Cui and deMontigny [16], and Hillal and Ismail [17].
In this research, a two–dimensional reaction rate/kinetics model is developed to assess and analyze the CO2 removal using aqueous 1DMA2P solution functioning under industrial relevant operating conditions. The intensification potential of the aqueous 1DMA2P solution for CO2 absorption by application of a polypropylene HFMC is estimated and validated in comparison with other solvents such as monoethanolamine (MEA), diethanolamine (DEA), methyldiethanolamine (MDEA), piperazine (PZ) and 4-(diethylamino)-2-butanol (DEAB) solutions. Also, the impact of essential parameters on the CO2 removal have been determined.
Section snippets
Gas-liquid absorption by membrane technology
In the membrane separation technology which considered in the present work, the gas and liquid streams pass through independent parts of contactor with independent flow rates and counter–current operation mode. Module inner diameter (R) is 63.50 mm and total number of fibers are 3600. The gas stream enters a shell with a diameter of 0.529 mm at a pressure of 200 kPa and a velocity of 1 mm/s and the liquid stream enters a tube with an internal diameter of 0.22 mm. Module have 3600 fiber with
Kinetic investigation
Donaldson and Nguyen [18] developed a base-catalyzed hydration mechanism for CO2 absorption in tertiary amine solutions. According to this mechanism, the tertiary amines catalyze the hydration reaction of CO2. The reaction mechanism between CO2 and aqueous 1DMA2P solution and also, required kinetic and equilibrium data are as follows [5,6,[19], [20], [21], [22]]:
The K for
Model development
The CO2/N2 gas mixture (20 vol.% / 80 vol.%) enters the shell side of the contactor, while 1DMA2P solution flows through the tube side, in co- or counter-current operational modes. The mathematical model is assembled for non−wetted membrane mode on the following assumptions: steady state condition, ideal behaviors of gas mixture, laminar flow in the shell and tube sides, fully developed velocity profile in the shell and tube sides of HFMC. The material balance equations on different sections of
Model validation
Due to limited investigations about 1DMA2P solvent, the model is validated with reported experimental data on CO2 removal using common industrial solution such as MEA, DEA and MDEA [28,29]. Fig. 2-a illustrates the CO2 absorption flux from a gas mixture of CO2 and N2 into DEA and MDEA solutions versus CO2 partial pressure at atmospheric pressure. Comparison of reported results in this figure confirms that the deviation of model predicted results from the experimental data is acceptable [28].
Conclusions
The CO2 removal by novel reactive 1DMA2P solution was comprehensively studied in a HFMC under non-wetted condition. The effects of important operating parameters on the absorption performance of HFMC were evaluated at temperature of 298–313 K, solvent circulation velocity of 0.01–0.10 m/s, gas stream velocity of 0.01–0.20 m/s, 1DMA2P concentration of 0.5–2.5 M and number of fibers of 500–4000. The predicted results based on two–dimensional non–isothermal stationary model indicated that the CO2
Authors contributions
1- Dr. Majid Saidi
Contributions: Process modeling, analyzed data and write the paper.
2- Mr. Ebrahim Balaghi Inaloob
Contributions: Analyzed data, process modeling
Declaration of Competing Interest
The authors declare that they have no conflict of interest.
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