(Vapour + liquid) equilibria (VLE) of CO2 in aqueous solutions of 2-amino-2-methyl-1-propanol: New data and modelling using eNRTL-equation

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Abstract

This work presents new experimental results for carbon dioxide (CO2) solubility in aqueous 2-amino-2-methyl-1-propanol (AMP) over the temperature range of (298 to 328) K and CO2 partial pressure of about (0.4 to 1500) kPa. The concentrations of the aqueous AMP lie within the range of (2.2 to 4.9) mol · dm−3. A thermodynamic model based on electrolyte non-random two-liquid (eNRTL) theory has been developed to correlate and predict the (vapour + liquid) equilibrium (VLE) of CO2 in aqueous AMP. The model predictions have been in good agreement with the experimental data of CO2 solubility in aqueous blends of this work as well as those reported in the literature. The current model can also predict speciation, heat of absorption, enthalpy of CO2 loaded aqueous AMP, pH of the loaded solution, and AMP volatility.

Highlights

► (Vapour + liquid) equilibria of CO2 in aqueous AMP are measured in an equilibrium cell. ► Electrolyte-NRTL equation with RKS EoS is used to model VLE of CO2 in (AMP + H2O). ► The model is validated against experimental data of this work and literature data. ► The current model also predicts heat of absorption, pH and amine volatility. ► Aqueous AMP can be a good solvent for CO2 capture from coal power plant flue gas.

Introduction

Removal of acid gas impurities, such as carbon dioxide (CO2) and hydrogen sulphide (H2S), from natural gas, refinery off-gases, hydrogen, and synthesis gas for ammonia production is an important operation in industrial gas processing. Besides, growing environmental concerns today for global warming and climate change have motivated extensive research activities towards developing more efficient and improved processes for CO2 capture from large point sources of CO2. The widely used processes for the removal of CO2 from natural gas and industrial gas streams are the regenerative absorption of CO2 into aqueous solutions of alkanolamines. Commercially important alkanolamines used for this purpose are monoethanolamine (MEA), diethanolamine (DEA), N-methyldiethanolamine (MDEA), and 2-amino-2-methyl-1-propanol (AMP) [1]. The gas streams in these processes are usually at high pressures of about 3 to 10 MPa. But, the major challenges for CO2 capture from fossil fuel based power plants are the large volumetric flow rates of flue gas at essentially atmospheric pressure with large amount of CO2 at low partial pressures. The presence of SOx, NOx, and significant oxygen partial pressure in the flue gas from coal based power plants gives rise to further problems for implementation of the amine absorption process for CO2 capture from power plant flue gas streams. The MEA is considered suitable for flue gas cleaning because of its high reaction rate at low CO2 partial pressure and low raw material cost. However, the costs of absorption process using MEA are high because of the high energy consumption in regenerating and operation problems such as corrosion, solvent loss, and solvent degradation [2]. Furthermore, MEA can be loaded up to only 0.5 mol of CO2 per mol MEA as a result of the stable carbamates formed [3].

Sartori and Savage [4] reported a new class of amines, sterically hindered amines (SHA), that can be commercially attractive new absorbent for CO2 capture process. Sharma [5] observed that the steric effect influence the stability of the carbamates due to the amine-CO2 reaction and proposed the use of highly branched amines such as AMP for higher cyclic absorption capacity for CO2. As in MDEA, the CO2 loading in AMP approaches a value of 1.0 mol of CO2 per mole of amine, while the reaction rate constant for (CO2 + AMP) is much higher than that for (CO2 + MDEA). Since the sterically hindered amine does not form a stable carbamate, bicarbonate and carbonate ions may be present in the solution in larger amounts then carbamate ions [6]. Hence the cost of regeneration energy when aqueous solutions of AMP are used to absorb CO2 may be lower than when aqueous MDEA solutions are used. Zhang et al. [7] observed that a number of heat-stable salts (HSS) could cause a reduction in CO2 absorption capacity and regeneration efficiency. Their results indicate that AMP is easier to regenerate with less loss of absorption capacity than other amines, such as, MEA, diethanolamine (DEA), diethylenetriamine (DETA) and N-methyldiethanolamine (MDEA). According to them, the regeneration performance can be ranked in the following order: AMP > MDEA > DEA > MEA. Hence AMP is considered today as one of the most important sterically hindered amine for CO2 capture from natural gas as well as from power plant flue gas [3], [8], [9].

The VLE data of the (CO2 + amine + water) system at various temperatures and concentrations have a very important role in the design and optimisation of industrial gas treating process. In rate-based models, physical and chemical equilibria play an important role by defining the boundary conditions for the partial differential equations that describe mass transfer coupled with chemical reactions [10]. Besides, the equilibrium solubility of the CO2 in aqueous amine solutions determines the minimum recirculation rate of the solution that would treat a CO2-laden gas stream, and it determines the maximum concentration of CO2 which can be left in the regenerated solution in order to meet the treated gas specifications. Although aqueous AMP and AMP blends are extensively used in the purification of gas streams contaminated with CO2, a few results of CO2 solubility in aqueous AMP solutions have been reported earlier [11], [12], [13], [14]. However, there are some discrepancies noted among the published data. Modified Kent and Eisenberg modelling approach [15] has been used by Tontiwachwuthikul et al. [12], Li and Chang [16], Park et al. [17] to correlate their experimental data. Teng and Mather [11], Jene and Li [18] adopted Deshmukh and Mather model [19]. Silkenbäumer et al. [13], Kundu et al. [20] used an approach based on Pitzer’s–GE model to correlate the measured VLE data. However, in all the reported literature, the deviations between the measured and correlated results are quite high and lie in the range of 15% to 35%.

Reliable experimental data and a consistent thermodynamic model are still necessary to describe the thermodynamic equilibrium behaviour of CO2 in concentrated aqueous AMP over wide ranges of temperature and pressure. In view of this, the objective of this present work is to provide additional solubility data of CO2 in aqueous AMP over a wide range of concentration and at low to high CO2 partial pressure. A thermodynamic VLE model based on electrolyte non-random two-liquid (eNRTL) theory [21], [22], [23], [24] has also been developed to represent the equilibrium solubility of CO2 in aqueous AMP. Besides, this model is also needed to represent the VLE of CO2 in activated and blended aqueous AMP solvents. In this work Aspen Plus® software, V-7.0 [25] has been used for data regression and model validation.

Section snippets

Materials

Reagent grade AMP (mass fraction purity > 0.95) is supplied by E. Merck, Germany and is used without further purification. Carbon dioxide (mass fraction purity > 0.999) is obtained from Chemtron Science Pvt. Ltd., India. Double distilled water degassed by prolonged boiling and cooled to ambient temperature under air tight conditions was used to prepare aqueous amine solutions. The 1 M (mol · dm−3) standard solutions of aqueous HCL and NaOH were obtained from Merck, India. The amine concentration is

Chemical and phase equilibria

In the aqueous phase for the (AMP + CO2 + H2O) system, the following chemical equilibria are involved [3], [20]2H2K1H3O+OH-CO2+2H2OK2H3O++HCO3-HCO3-+H2K3H3O++CO32-AMP+H2OK4AMPH++OH-Each of the above chemical equilibrium is characterised by thermodynamic equilibrium constant (Kj; j = 1,  , 4) defined in terms of activity (ai):lnKj=iνi,jlnai,where νi,j is the reaction stoichiometric coefficient of component i in jth reaction. The temperature dependency of the equilibrium constants defined in

Equilibrium CO2 partial pressure

For validation of the measurement procedure, the experimental method and set up are standardised by measuring equilibrium solubility data of CO2 in aqueous DEA. The experimental data for the CO2 solubility in 3.5 mol · dm−3 (35 mass%) aqueous DEA at T = 323 K obtained in this work have been compared with data published by Lee et al. [35] in figure 1 (and table S1 in Supplementary material). It is evident from figure 1 that, the measurement of this work agrees well with the data reported by Lee et al.

Conclusions

In this work, new experimental results of VLE of CO2 in aqueous AMP from T = (298 to 328) K and in the equilibrium CO2 loading of (0.2 to 1.1) have been presented. The AMP concentrations of (2.5, 3.4, and 4.9) mol · dm−3 have been considered. A thermodynamic model based on eNRTL equation has been developed to predict VLE of CO2 in aqueous AMP. The results predicted by VLE model are in good agreement with the experimental results of this work and those reported in literature. This model also predicts

References (40)

  • J. Gabrielsen et al.

    Chem. Eng. Sci.

    (2007)
  • P. Zhang et al.

    J. Environ. Sci.

    (2008)
  • A. Samanta et al.

    Chem. Eng. Sci.

    (2009)
  • W.-J. Choi et al.

    Green Chem.

    (2007)
  • M. Kundu et al.

    J. Chem. Eng. Data

    (2003)
  • M.L. Posey et al.

    Ind. Eng. Chem. Res.

    (1997)
  • G. Soave

    Chem. Eng. Sci.

    (1972)
  • C. Mathonat et al.

    J. Chem. Eng. Data

    (1997)
  • J.T. Cullinane et al.

    Fluid Phase Equilib.

    (2005)
  • H. Arcis et al.

    J. Chem. Thermodyn.

    (2009)
  • I. Kim et al.

    Chem. Eng. Sci.

    (2009)
  • A.L. Kohl et al.

    Gas Purification

    (1997)
  • J. Gabrielsen et al.

    AIChE J.

    (2006)
  • G. Sartori et al.

    Ind. Eng. Chem. Fundam.

    (1983)
  • M.M. Sharma, Ph.D. Thesis, University of Cambridge, Cambridge, U.K.,...M.M. Sharma

    Trans. Faraday Soc.

    (1965)
  • A.K. Saha et al.

    Chem. Eng. Sci.

    (1995)
  • S.K. Dash, A. Samanta, A.N. Samanta, S.S. Bandyopadhyay, Chem. Eng. Sci., in press,...
  • T.T. Teng et al.

    Can. J. Chem. Eng.

    (1989)
  • P. Tontiwachwuthikul et al.

    J. Chem. Eng. Data

    (1991)
  • D. Silkenbäumer et al.

    Ind. Eng. Chem. Res.

    (1998)
  • Cited by (0)

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