ArticlePDF Available

Ab Intio Calculations on Reaction Process of Piperazine Absorbing CO 2

Authors:

Abstract

The increasing amount of CO2 emitted to the atmosphere has a deep impact on the environment. It is urgent to take effective measures to reduce CO2 emissions from its intensive emission source. Chemical absorption is an effective way to cover the large reduction of CO2, and piperazine (PZ) is one of the amines that have good performance on CO2 capture. To make a deep understanding of the chemical mechanism of PZ absorbing CO2, computational studies on PZ chemically absorbing CO2 are discussed in this work using Density functional theory (DFT). Possible reaction pathways of PZ absorbing CO2 are analyzed. Due to the special chemical structure of PZ, the reaction processes can be divided into two parts, the process of (PZ+CO2)+PZ and (PZ+2CO2)+PZ. To make a good understanding of the reaction process, a comparison of that between PZ and MEA are discussed. The results show that PZ has lower forward and backward energy barriers than MEA in the zwitterion formation, but in the intermolecular hydrogen transfer process, PZ has higher forward and backward barriers than MEA. For the reaction process of PZ+2CO2, it can be stated as a two-step zwitterion formation with two transition states. For the following intermolecular hydrogen transfer of PZ(COO)2+PZ, the atom movements are similar to that of (PZCOO+PZ). All the discussions provide theoretical information of PZ chemical absorbing CO2.
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 organizing committee of GHGT-13.
doi: 10.1016/j.egypro.2017.03.1346
Energy Procedia 114 ( 2017 ) 2121 2127
ScienceDirect
13th International Conference on Greenhouse Gas Control Technologies, GHGT-13, 14-18
November 2016, Lausanne, Switzerland
Ab Intio Calculations on Reaction Process of Piperazine Absorbing
CO2
Tingting Zhang 1,2, Yunsong Yu 1, Guoxiong Wang 3, Zaoxiao Zhang 1, 2,
*
1. School of Chemical Engineering and Technology, Xi’an Jiaotong University
No.28 Xianning West Road, Xi’an 710049, P.R. China
2. State Key Laboratory of Multiphase Flow in Power Engineering, Xi’an Jiaotong University
No.28 Xianning West Road, Xi’an 710049, P.R. China
3. School of Chemical Engineering, University of Queensland, Brisbane, Qld. 4072, Australia
Abstract
The increasing amount of CO2 emitted to the atmosphere has a deep impact on the environment. It is urgent to take effective
measures to reduce CO2 emissions from its intensive emission source. Chemical absorption is an effective way to cover the large
reduction of CO2, and piperazine (PZ) is one of the amines that have good performance on CO2 capture. To make a deep
understanding of the chemical mechanism of PZ absorbing CO2, computational studies on PZ chemically absorbing CO2 are
discussed in this work using Density functional theory (DFT).
Possible reaction pathways of PZ absorbing CO2 are analyzed. Due to the special chemical structure of PZ, the reaction processes
can be divided into two parts, the process of (PZ+CO2)+PZ and (PZ+2CO2)+PZ. To make a good understanding of the reaction
process, a comparison of that between PZ and MEA are discussed. The results show that PZ has lower forward and backward
energy barriers than MEA in the zwitterion formation, but in the intermolecular hydrogen transfer process, PZ has higher forward
and backward barriers than MEA. For the reaction process of PZ+2CO2, it can be stated as a two-step zwitterion formation with
two transition states. For the following intermolecular hydrogen transfer of PZ(COO)2+PZ, the atom movements are similar to
that of (PZCOO+PZ). All the discussions provide theoretical information of PZ chemical absorbing CO2.
© 2017 The Authors. Published by Elsevier Ltd.
Peer-review under responsibility of the organizing committee of GHGT-13.
Keywords: CO2 absorption, Piperazine, Reaction mechanism, DFT, Energy barriers
* Corresponding author. Tel.: +86-29-82660689; fax: +86-29-82660689.
E-mail address: zhangzx@mail.xjtu.edu.cn
Available online at www.sciencedirect.com
© 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 organizing committee of GHGT-13.
2122 Tingting Zhang et al. / Energy Procedia 114 ( 2017 ) 2121 – 2127
1. Introduction
The large amount of greenhouse gases emitted to the atmosphere has aroused many worldwide environmental
problems. Carbon dioxide (CO2) is recognized as a typical greenhouse gas. To alleviate these problem, intensive
researches on CO2 capture with energy-efficient method are of essential[1]. Chemical absorption is the commonly
used method, and amines are the typical absorbents, such as monoethanolamine(MEA), diethanolamine(DEA), N-
methyldiethanolamine (MDEA), and 2-amino-2-methyl-1-propanol (AMP)[2, 3]. Generally, primary and secondary
amines have fast reaction rate and high regeneration energy consumption, ternary and hinder amines have lower
regeneration energy consumption but slow reaction rate. Based on this, mixed solvents are discussed to take
advantage of the fast reactivity of primary or secondary amines and low solvent regeneration energy consumption of
tertiary or sterically hindered amines [4-6].
Among the discussed amines, piperazine (C4H10N2, PZ) was found to perform well with CO2 absorption in
mixing with the commonly used amines. The using of piperazine to activate aqueous MDEA solutions was patented
by BASF for its good application in the bulk removal of CO2 in ammonia plants. And at the temperature range of 40
to 60 °C, the mass transfer rate of CO2 into concentrated PZ is more than 1.5-2.0 times faster than MEA. And in the
presence of stainless steel materials, PZ has lower oxidative degradation than that of MEA[7, 8]. There are many
experimental works on the PZ performance at CO2 absorption, but limited works had been found about the detailed
reactions between CO2 and aqueous piperazine. Hence, to make a better understanding of the mechanism and
working principles of the absorption process, simulations discussions are discussed in this work.
The reaction mechanism of primary and secondary alkanolamines with CO2 can be described using the zwitterion
mechanism, as originally proposed by Caplow (1968)[9] and later reintroduced by Danckwerts (1979)[10]. The
chemical structure and amino group of piperazine is different from that of the typical alkanolamines, but the
chemical functional groups are same and they are all R-NH. The main chemical interaction between amino group
and CO2 are universal. It is assumed that this mechanism is applicable to PZ, though it is a diamine with cyclic
structure. However, the different chemical structures that connect with the amino functionality have influence on the
reaction configuration and reaction energy, of which has influence on the performance of CO2 absorption capacity
and energy consumption.
Combining the reaction processes of MEA absorbing CO2, it is assumed that piperazine first reacts with CO2 to
form a zwitterion. Then the zwitterion will be deprotonated by a base (here, PZ is the discussed base and all the
discussions in this work do not involved the H2O molecules) present in the liquid. As piperazine is a heterocycle and
has two amine groups, it has the potential to absorb two CO2 molecules at one time. Thus, the main reactions
discussed in this paper contain two parts, PZ+CO2 and PZ+2CO2. The reaction processes are shown in equations (1-
4),
2
PZ+CO PZCOOo
(1)
-+
PZCOO+PZ PZCOO +PZHo
(2)
222
CO +PZ+CO CO -PZCOO (COO)PZ(COO)oo
(3)
-+
22
PZ(COO) + PZ PZ(CO )COO +PZHo
(4)
The reaction processes of equation (1) and (2) are similar to that of MEA. The reaction processes of equation (3)
and (4) are special ones for PZ. The reaction process of equation (2) is compared with that of equation (4) to find out
the effect of the extra CO2 molecule on the reaction process. Based on those analyses, we will finally find out the
reaction properties of PZ chemically absorbing CO2.
Tingting Zhang et al. / Energy Procedia 114 ( 2017 ) 2121 – 2127 2123
2. Computational details
The simulation works were performed with Gaussian 09 software using density functional theory (DFT). The
chemical interactions of PZ absorbing CO2 were studied in aqueous solvation effect with pauling atomic radii. The
optimized geometries and frequencies of the reactants, transition states and products were obtained at the B3LYP/6-
311G++(d, p)//B3LYP/6-311G level. The transition states have only one imaginary frequency and the vibrational
mode is consistent with the reactant and product. The IRC (Intrinsic reaction coordinate) and Gibbs free energy are
calculated to analyze the reaction. The reaction energies is defined as: ΔEreaction = Eproducts-Ereactants, where ΔEreaction is
the energy difference between products and reactants for the corresponding reaction process, Eproducts and Ereactants are
the energy of products and reactants, respectively[11].
3. Result and discussions
In the reaction process of PZ absorbing CO2, zwitterion formation and the followed hydrogen transfer as shown
in eqs (1-4) are the main reaction mechanism. The atom movements (ie. N-C bond) were discussed. Fig. 1(a) gives a
comparison of structure between MEA and PZ, and it clearly demonstrates the typical geometry difference between
MEA (an industry standard alkanolamine) and PZ (circle structure).
3.1. PZ+CO2 and the following hydrogen transfer
Fig. 1(b) shows the main atom movements of PZ absorbing CO2 in zwitterion formation. The C-N bond lengths
are marked in the figure. As the zwitterion formed, the following reaction step is the hydrogen transfer. In the
process of zwitterion PZCO2 reacting with another PZ molecule, hydrogen atom moves from zwitterion to the
second PZ, and finally produce PZCOO- and PZH+, and this is an intermolecular hydrogen transfer process.
To make a good understanding of the reaction process and energy changes of this process, a comparison between
PZ and MEA is made as the process of MEA absorbing CO2 were also simulated at the same calculation level. The
energy changes are shown in Fig. 2. The results show that in the zwitterion formation, the IRC and Gibbs free
energy barriers of PZ are lower than those of MEA no matter in the forward and backward processes. The forward
Gibbs free energy barriers are much higher than the backward ones, and the energy gaps are 24kJ/mol both for PZ
and MEA. For the IRC, the backward energy barriers are higher than those forward ones, the energy gaps are more
than 3kJ/mol both for PZ and MEA. For the followed hydrogen transfer process, seen from Fig. 2, the backward
energy barriers are much higher than the forward processes for PZ and MEA. Compared the results of PZ and MEA,
the IRC and Gibbs free energy barriers of PZ are higher than those of MEA for both forward and backward
processes.
Combining the zwitterion formation and the following intermolecular hydrogen transfer, the reaction energy
barriers show that in PZ absorbing CO2 process, the zwitterion formation is the dominant reaction unit during the
reaction pattern of (PZ+CO2)+PZ. Thus, small reaction energy barrier advantage is observed for PZ over MEA in in
the reaction pattern of (RNH+CO2)+RNH. However, for the desorption process, the hydrogen transfer process is the
dominant unit and MEA has lower energy barriers than PZ.
3.2. CO2+PZ+CO2 series and the following hydrogen transfer
As a diamine, one PZ has the potential to absorb two CO2 at the same time. The complex reaction process of
PZ+2CO2 can be summarized as a two-step zwitterion formation with two transition states, as shown in Fig. 1(c). It
includes the reaction unit of series1 to series 3 through series/TS 2 and series 3 to series 5 through series/TS 4. The
reaction energy changes are shown in Fig. 3. The IRC energy change of the five states is regular, that is the
transition state has higher relative energy over the corresponding reactant and product. For the reaction process of
the first zwitterion, the Gibbs energy of series/TS 4 is higher than that of series 1 and series 3. However, for the
second zwitterion formation of series 3 to series 5 through series/TS 4, the Gibbs free energy increases from series 3
2124 Tingting Zhang et al. / Energy Procedia 114 ( 2017 ) 2121 – 2127
to series 5 as shown in Fig. 3. Hence, for the two-step zwitterion formation of PZ+2CO2, series 3 is a rational
reaction product while the series 5 may not easily exist in the solution at the discussed temperature (298.15K).
Comparing the zwitterion formation of series 1 to series 3 in (CO2+PZ+CO2) with that in (PZ+CO2) process, the
forward Gibbs free energy is higher in the process of PZ+2CO2 than that in PZ+CO2. And for the IRC energy
barriers and the backward Gibbs free energy barrier, there is no significant different between these two reaction
processes. Thus, the zwitterion formation process of series 1 to series 3 is similar to that of zwitterion formation of
(PZ+CO2) for the similar atom movements and reaction energy barriers, and the extra CO2 atom has no significant
effect on the zwitterion formation.
4.31
4.28
4.31 2.22
4.31 1.64
1.64
2.15
1.66
1.66
Series 1
Series/TS 2
Series 3
Series/TS 4
Series 5
4.32
2.22
1.63
(b) Zwitterion formation
PZ MEA
(c) CO2+PZ+CO2reaction series
(a) PZ and MEA molecular structure
Fig. 1. The typical structure for MEA and PZ
Tingting Zhang et al. / Energy Procedia 114 ( 2017 ) 2121 – 2127 2125
0.0 0.5 1.0 1.5 2.0 2.5 3.0 3.5 4.0 4.5 5.0 5.5 6.0
-30
-20
-10
0
10
20
30
40
Energy change ( kJ/mol)
Reaction Coordinate
PZ,IRC
PZ,Gibbs
MEA,IRC
MEA,Gibbs
15.10
17.81
31.33
38.77
0.00
-4.01
-3.70
24.39
29.37
0.00
-27.04
-19.11
-23.23
-17.81
0.84
3.78
4.05
6.93
Zwitterion formation Intermolecular hydrogen transfer
Fig. 2. Comparison of energy barrier on the reaction process of zwitterion and hydrogen transfer process
Series 1 Series/TS 2 Series 3 Series/TS 4 Series 5
0
10
20
30
40
50
60
70
1.11
72.08
13.05
67.18
-4.29
32.45
14.83
39.68
PZ+2CO2,IRC
PZ+2CO2,Gibbs
Reaction Energy Barrier (kJ/mol)
Reaction Coordinate
0.00
Fig. 3. The reaction energy changes for the PZ reacting with two CO2 process
2126 Tingting Zhang et al. / Energy Procedia 114 ( 2017 ) 2121 – 2127
20.399
1.384
1.245
1.462
1.185
3.389
B3LYP/6-311G B3LYP/6-311G++(d,p)
Fig. 4. The transition states geometry under different base set (the unit of the bond is Å)
In the above discussed series reaction process, the formed zwitterion can react with another PZ molecule to
produce the PZ(COO)COO- anion and PZH+ cation. The series 3 is a rational product and then could react with the
second PZ molecule. And during the simulation process, it was observed that with different calculation base set, the
optimized geometry of the transition state is different which is shown in Fig. 4. The typical bond lengths are marked.
The relative situation of H atom is a little different in these two geometry, and the significant different structure is
the bond length of N-C between PZ and the extra CO2 molecule, which is 3.389 Å at the base set of B3LYP/6-311G
and 20.399 Å at the base set of B3LYP/6-311G++(d, p).
The reaction energies at the calculating base set of B3LYP/6-311G++(d, p) are used to analyze the energy
barriers. The forward IRC energy barrier is 6.67kJ/mol and the backward is 34.17kJ/mol. The results are very
similar to that of the (PZCOO+PZ) hydrogen transfer process, which are 6.93kJ/mol for the forward and
33.97kJ/mol for the backward process. For the Gibbs free energy, the forward barrier is 6.17kJ/mol and the
backward is 28.64kJ/mol, while they are 4.05 kJ/mol and 23.16kJ/mol, respectively in the (PZCOO+PZ) hydrogen
transfer process. Hence, in those two intermolecular hydrogen transfer processes, the extra CO2 molecule has little
impact on the atom movements of the reaction but the forward and backward Gibbs free energy barriers become
higher.
4. Conclusions
The main reactions and possible pathways of PZ absorbing CO2 are analyzed in aqueous solutions and H2O
molecules are not involved in the chemical reactions. The corresponding reaction energies are calculated using the
ab initio simulations. Zwitterion formation and the followed intermolecular hydrogen transfer processes are the main
reaction paths. Due to the special chemical structure of PZ, the reaction processes can be divided into two parts, the
process of (PZ+CO2)+PZ and (PZ+2CO2)+PZ. In the discussion of (PZ+CO2)+PZ, to make a good understanding of
the reaction process, a comparison of that between PZ and MEA are discussed. The results show that PZ has lower
forward and backward energy barriers than MEA in the zwitterion formation, but in the intermolecular hydrogen
transfer process, PZ has higher forward and backward barriers than MEA. As the energy barriers of zwitterion
formation are much higher than those of the intermolecular hydrogen transfer in the forward reaction process, it can
be concluded that in the absorption process, PZ can absorb CO2 with lower energy consumption than MEA
theoretically. For the reaction process of PZ+2CO2, higher forward and backward Gibbs free energy barriers are
observed in the first zwitterion formation (series 1 to series 3 through series/TS 2) than that in PZ+CO2. The second
zwitterion formation of series3 to series 5 is turns out to be a rational IRC energy change but the Gibbs free energy
is sustained increasing. For the following intermolecular hydrogen transfer of (PZ(COO)2+PZ), the atom movements
are similar to that of (PZCOO+PZ), but the forward and backward energy barriers are a bit higher than that of
(PZCOO+PZ) both for IRC and Gibbs free energy barrier. All those discussions provide theoretical information and
better understanding of PZ chemical absorbing CO2. And further works about the effect of H2O molecules on the
reactions are needed.
Tingting Zhang et al. / Energy Procedia 114 ( 2017 ) 2121 – 2127 2127
Acknowledgements
This work is financially supported by the National Natural Science Foundation of China (No. 51276141).
References
[1] IEA. World Energy Outlook Special Report on Energy and Climate Change. International Energy Agency (IEA); 2015. p. 115-22.
[2] Rochelle GT. Amine scrubbing for CO2 capture. Science. 2009;325:1652-4.
[3] Mumford KA, Wu Y, Smith KH, Stevens GW. Review of solvent based carbon-dioxide capture technologies. Frontiers of Chemical Science
and Engineering. 2015;9:125-41.
[4] Sun W-C, Yong C-B, Li M-H. Kinetics of the absorption of carbon dioxide into mixed aqueous solutions of 2-amino-2-methyl-l-propanol and
piperazine. Chemical Engineering Science. 2005;60:503-16.
[5] Du Y, Yuan Y, Rochelle GT. Capacity and absorption rate of tertiary and hindered amines blended with piperazine for CO2 capture. Chemical
Engineering Science. 2016;155:397-404.
[6] Edali M, Aboudheir A, Idem R. CO2 absorption into MDEA/PZ using 2-D absorption-rate kinetic model. Reactions.9:9.
[7] Yeon SH, Sea B, Park YI, Lee KS, Lee KH. Absorption of Carbon Dioxide Characterized by Using the Absorbent Composed of Piperazine
and Triethanolamine. Separation Science and Technology. 2004;39:3281-300.
[8] Max Appl D-S, Ulrich Wagner L, Hans J. Henrici M, Klaus Kuessner H, Klaus Volkamer F, Ernst Fuerst N, all of Fed. Rep. of Germany.
Removal of CO2 and/or H2S and/or COS from gases containing these constituents. In: Patent US, editor.: BASF Aktiengesellschaft, Fed. Rep.
of Germany; 1982.
[9] Caplow M. Kinetics of carbamate formation and breakdown. Journal of the American Chemical Society. 1968;90:6795-803.
[10] Danckwerts PV. The reaction of CO2 with ethanolamines. Chemical Engineering Science. 1979;34:443-6.
[11] Xie HB, Zhou Y, Zhang Y, Johnson JK. Reaction Mechanism of Monoethanolamine with CO2 in Aqueous Solution from Molecular
modeling. The Journal of Physical Chemistry A. 2010;114:11844-52.
ResearchGate has not been able to resolve any citations for this publication.
Article
Full-text available
Currently, a large proportion of global fossil fuel emissions originate from large point sources such as power generation or industrial processes. This trend is expected to continue until the year 2030 and beyond. Carbon capture and storage (CCS), a straightforward and effective carbon reduction approach, will play a significant role in reducing emissions from these sources into the future if atmospheric carbon dioxide (CO2) emissions are to be stabilized and global warming limited below a threshold of 2 °C. This review provides an update on the status of large scale integrated CCS technologies using solvent absorption for CO2 capture and provides an insight into the development of new solvents, including advanced amine solvents, amino acid salts, carbonate systems, aqueous ammonia, immiscible liquids and ionic liquids. These proposed new solvents aim to reduce the overall cost CO2 capture by improving the CO2 absorption rate, CO2 capture capacity, thereby reducing equipment size and decreasing the energy required for solvent regeneration. © 2015, Higher Education Press and Springer-Verlag Berlin Heidelberg.
Article
Full-text available
The rate law for reaction of amines with carbon dioxide is rate = kamine(R2NH)(CO2) + kamine′(R2NH)· (OH)(CO2), where the first and second terms are for uncatalyzed and hydroxide-catalyzed pathways. The latter reaction, which involves proton abstraction in the rate-determining step, is not observed with all amines. Values for kamine at 10° follow the Brønsted relationship log kamine (M-1 sec-1) = mpK + Y, with values of m and Y equal to 0.43 and -1.50 for reactions of primary and secondary amines, and 0.48 and -0.20 for the reactions of hydrazine and hydroxylamine derivatives. Second-order rate constants for hydrogen ion catalyzed decarboxylation of carbamates formed from amines of pK -1.05 to approximately 5 may be fitted to a Brønsted relationship log kH + (M-1 sec-1) = 0.77pK + 3.6 at 10°. Rates for carbamates formed from more basic amines are virtually independent of basicity and are approximately 108 M-1 sec-1. The rate-limiting step in carbamate formation and breakdown with weakly basic amines involves carbon-nitrogen bond formation and cleavage. It is suggested that proton transfer may be rate limiting in the synthesis and breakdown of carbamates formed from basic amines.
Article
Full-text available
We present a theoretical study of the reaction mechanism of monoethanolamine (MEA) with CO₂ in an aqueous solution. We have used molecular orbital reaction pathway calculations to compute reaction free energy landscapes for the reaction steps involved in the formation of carbamic acids and carbamates. We have used the conductor-like polarizable continuum model to calculate reactant, product, and transition state geometries and vibrational frequencies within density functional theory (DFT). We have also computed single point energies for all stationary structures using a coupled cluster approach with singles, doubles, and perturbational triple excitations using the DFT geometries. Our calculations indicate that a two-step reaction mechanism that proceeds via a zwitterion intermediate to form carbamate is the most favorable reaction channel. The first step, leading to formation of the zwitterion, is found to be rate-determining, and the activation free energies are 12.0 (10.2) and 11.3 (9.6) kcal/mol using Pauling (Bondi) radii within the CPCM model at the CCSD(T)/6-311++G(d,p) and CCSD(T)/6-311++G(2df,2p) levels of theory, respectively, using geometries and vibrational frequencies obtained at the B3LYP/6-311++G(d,p) level of theory. These results are in reasonable agreement with the experimental value of about 12 kcal/mol. The second step is an acid-base reaction between a zwitterion and MEA. We have developed a microkinetic model to estimate the effective reaction order at intermediate concentrations. Our model predicts an equilibrium concentration for the zwitterion on the order of 10⁻¹¹ mol/L, which explains why the existence of the zwitterion intermediate has never been detected experimentally. The effective reaction order from our model is close to unity, also in agreement with experiments. Complementary ab initio QM/MM molecular dynamics simulations with umbrella sampling have been carried out to determine the free energy profiles of zwitterion formation and proton transfer in solution; the results confirm that the formation of the zwitterion is rate-determining.
Article
Aqueous piperazine (PZ) blended with a tertiary or hindered amine combines the high CO2 capacity of the tertiary or hindered amine with the fast rate of PZ. For flue gas CO2 capture, the optimum pKa (that which offers the highest CO2 cyclic capacity) of a mono-tertiary amine blended with PZ is 9.1. A generic Aspen Plus® model for PZ/tertiary amine was developed to predict the CO2 vapor-liquid-equilibrium (VLE) from the pKa of the tertiary amine. The polarity of the tertiary amine also affects the CO2 solubility of the PZ/tertiary amine. Hindered amines that form little carbamate show similar CO2 VLE to tertiary amines with the same pKa, when blended with PZ. The CO2 absorption rate of most 2.5 m PZ/2.5 m tertiary amines was slightly slower than 2.5 m PZ, probably due to the higher viscosity of the blends.
Article
An aqueous solution containing from 0.81 to 1.3 moles of piperazine per liter is used as a washing agent for removing impurities such as h2s, co2 and cos from gases. Piperazine can also be used, in amounts of up to 0.8 mole per liter, together with physical or chemical solvents, to accelerate the absorption of h2s, co2 and cos. The washing process is used for natural gases, coke-oven gases, gases from the gasification of coal and synthesis gases, of any origin.
Article
Measurements of the rates of homogeneous reaction of mono-, di- and tri-ethanolamine by various workers are critically compared. Some discrepancies remain unexplained but it seems probable that a zwitterion is the intermediate in the formation of carbamate and that the reaction of DEA (but not of MEA) is catalysed by bases.
Article
This work studies the CO2 absorption of alkanolamine, piperazine, and TEA (triethanolamine), and the chemical reaction kinetics of CO2 by using the mixed solution of piperazine and TEA in polyvinylidine‐fluoride hollow fiber membrane contactor‐stripper hybrid process. Absorption was studied from 303K to 382K in the mixed solution of piperazine 0.26 M, 0.64 M, and TEA 0.38 M, 1.13 M, 2.26 M. Also, absorption rates were measured as a function of CO2 partial pressure in the mixed solutions. The increase of the initial absorbent concentration and CO2 partial pressure showed a high absorption rate of CO2. Our experiment revealed that the absorption capacity of the mixed absorbent of TEA and piperazine with CO2 was mostly governed by the piperazine concentration. The TEA is a tertiary amine with low CO2 absorption capacity, but it helps the hollow fiber membrane keep the non‐wetting condition in the fiber's pores because of the high viscosity of TEA. Therefore, the addition of piperazine to TEA, which has too low absorption capacity with CO2, makes it possible to obtain a high CO2 removal efficiency. Finally, the kinetic data on the reaction of piperazine and CO2 were investigated, and the activation energy was calculated through the Arrhenius expression.
Article
The reaction kinetics of the absorption of CO2 into aqueous solutions of piperazine (PZ) and into mixed aqueous solutions of 2-amino-2-methyl-l-propanol (AMP) and PZ were investigated by wetted wall column at 30–40 °C. The physical properties such as density, viscosity, solubility, and diffusivity of the aqueous alkanolamine solutions were also measured. The N2O analogy was applied to estimate the solubilities and diffusivities of CO2 in aqueous amine systems. Based on the pseudo-first-order for the CO2 absorption, the overall pseudo first-order reaction rate constants were determined from the kinetic measurements. For CO2 absorption into aqueous PZ solutions, the obtained second-order reaction rate constants for the reaction of CO2 with PZ are in a good agreement with the results of Bishnoi and Rochelle (Chem. Eng. Sci. 55 (2000) 5531). For CO2 absorption into mixed aqueous solutions of AMP and PZ, it was found that the addition of small amounts of PZ to aqueous AMP solutions has significant effect on the enhancement of the CO2 absorption rate. For the CO2 absorption reaction rate model, a hybrid reaction rate model, a second-order reaction for the reaction of CO2 with PZ and a zwitterion mechanism for the reaction of CO2 with AMP was used to model the kinetic data. The overall absolute percentage deviation for the calculation of the apparent rate constant kapp is 7.7% for the kinetics data measured. The model is satisfactory to represent the CO2 absorption into mixed aqueous solutions of AMP and PZ.
Article
Amine scrubbing has been used to separate carbon dioxide (CO2) from natural gas and hydrogen since 1930. It is a robust technology and is ready to be tested and used on a larger scale for CO2 capture from coal-fired power plants. The minimum work requirement to separate CO2 from coal-fired flue gas and compress CO2 to 150 bar is 0.11 megawatt-hours per metric ton of CO2. Process and solvent improvements should reduce the energy consumption to 0.2 megawatt-hour per ton of CO2. Other advanced technologies will not provide energy-efficient or timely solutions to CO2 emission from conventional coal-fired power plants.
CO2 absorption into MDEA/PZ using 2-D absorption-rate kinetic model
  • M Edali
  • A Aboudheir
  • R Idem
Edali M, Aboudheir A, Idem R. CO2 absorption into MDEA/PZ using 2-D absorption-rate kinetic model. Reactions.9:9.