Ze Sun*,
Jia Wang,
Wei Du,
Guimin Lu,
Ping Li,
Xingfu Song and
Jianguo Yu
National Engineering Research Center for Integrated Utilization of Salt Lake Resource, East China University of Science and Technology, Shanghai 200237, China. E-mail: zsun@ecust.edu.cn; Fax: +86-21-64252826; Tel: +86-21-64250981
First published on 13th April 2016
Reducing CO2 emission is one of the most important events to solve the global climate problem. The carbonation reaction of CaO and the reverse reaction are potential methods for CO2 capture and concentration from dilute flue gases at high temperature. In this paper, the thermodynamics and mechanisms of CO2 capture by CaO and CaO regeneration from CaCO3 were studied and identified in the framework of density functional theory (DFT). In the calculation, the exchange-correlation term was approximated by Perdew–Wang (PW91), a function within the generalized gradient approximation (GGA) family. The reaction energies of carbonation reaction and calcination reaction were calculated to be −147.64 kJ mol−1 and 180.60 kJ mol−1, respectively. To study the reaction between CO2 and CaO, the transition states of carbonation and calcination were also analyzed. The results showed that the carbonation of CaO was rather fast, and the activation energy of carbonation reaction was 0 kJ mol−1, which indicated that the reaction process was not the rate-determining step during the process of CO2 capture. The regeneration of CaO by CaCO3 calcination occurred at higher temperature, with the activation energy of 166.85 kJ mol−1, and the rate of calcination was controlled by the chemical reaction.
CO2 separation from dilute gas is the first and most energy intensive step, and many efforts have been devoted to developing new methods for CO2 capture and separation. Current CO2 capture technologies mainly include solid sorbent absorption, liquid solvent absorption, membrane separation, distillation of a liquefied gas stream and refrigerated separation.8,9 Processes utilizing simple sorbents, e.g., limestone or dolomite, have significant advantages given the relatively low cost, abundance, and availability of these materials. Ca-based sorbents can be used for CO2 capture,10 whose application in fluidized bed conversion systems has received increasing attention recently.11–14
CO2 can be separated through a multicycle process via the carbonation reaction of CaO with the CO2 from flue gas and then the regeneration of the sorbent CaO through CaCO3 calcination reaction in a fluidized bed, as illustrated in Fig. 1.14 The background of this method dates back to 1967, when DuMotay and Marechal first patented the use of lime to aid the gasification of carbon by steam.15 This process consists of two fluidized bed reactors, carbonator and calciner, which are connected by solid transport pipes. After reaction, CO2-clean flue gas exiting in the carbonator is released to the atmosphere, while the product CaCO3 is transported to the calciner to regenerate CaO and produce pure CO2 stream. The regenerated CaO is then transported back to the carbonator for cycle use, while the CO2 released from the regenerator is concentrated enough to be purified, compressed, and stored.
The process proposed above happens at high temperature, and the reversible chemical reactions16,17 are expressed as eqn (1) and (2).
![]() | (1) |
![]() | (2) |
The CO2 capture efficiency could achieve 95% for this method.16 The carbonation reaction is exothermic, while the reverse one is endothermic, so the energy can be efficiently used in a steam cycle.18
The carbonation reaction is a typical gas–solid reaction with the formation of a solid product. The reaction involves two quite different stages: a fast one taking minutes at first, kinetically controlled, and a slow stage, controlled by diffusion through the layer formed, which lasts hours to days.19 Based on the nature of the reaction, it seems that a pure chemical reaction controlling regime is very short and can be neglected without much error in the mathematical modeling.20
For calcination reaction, three possible rate-limiting processes have been proposed: (1) heat transfer through the particle to the reaction interface; (2) mass transfer of the CO2 released from the reaction surface through the porous system, and (3) chemical reaction. However, mass transfer or chemical reaction has been considered as the rate-limiting process by most authors.21
To improve the design of carbonation–calcination fluidized bed and to increase CO2 capture efficiency, it is imperative to make clear of the rate-controlling steps for both reactions. To reveal which roles the chemical reactions play in the carbonation/calcination processes, this work mainly focuses on the thermodynamics and mechanisms of CaO carbonation process and CaO regeneration process through density functional theory (DFT). It is difficult to model reaction mechanisms by experiments, however, theoretical calculation can do it efficiently on molecular or atomic level. The mechanisms of reductive decompositions of CaSO4 by CO and CH4 have been proposed through computer simulation, and the calculated activation energies were in good agreement with experimental values, which confirmed the validity of computer simulation and density functional theory (DFT).22,23 DFT calculations can also provide a satisfied estimation of the relative stability of different surfaces and surface reactions,24 especially with modern functions.25 Here, the micro-processes, activation energies and reaction energies of the two reactions were analyzed through DFT calculation, to support the development of CO2 capture concepts and to improve the design of the fluidized bed as outlined in Fig. 1.
The surface energy of CaO and CaCO3 were calculated to select the reaction surface, the calculation process would be described in detail in section 3. As a result, the (100) and (110) surfaces were determined for CaO and CaCO3, respectively. Here, (100) surface refers to the crystal face which is parallel to the yz plane and (110) refers to the crystal face parallel to the z crystal axis. To avoid the interactions between periodic images with the surface, a vacuum region of 15 Å was added above the surface. All the structures were first relaxed thoroughly before reaction calculations.
To search the transition state (TS), linear synchronous transit/quadratic synchronous transit (LST/QST) algorithm was used. First, the LST optimization was performed, doing an LST maximization, which followed by an energy minimization in directions conjugate to the reaction pathway, to yield a structure lower in energy and closer to the true TS, namely approximated TS. Secondly, QST maximization was performed on the approximated TS, with another conjugate gradient minimization performed. The cycle was repeated until a stationary point was located. Then the calculation of the activation energies for carbonation of CaO and calcination of CaCO3 could be completed. All the optimized structures were considered to be stable with the only one imaginary frequency for TS structures.
The activation energy and reaction energy are defined as eqn (3) and (4) respectively:
Ea = ETS − ER | (3) |
E = EP − ER | (4) |
The optimization of isolated CO2 molecule was performed in a large cubic box of 10 × 10 × 10 Å. The calculated bond length was 1.175 Å, while the experimental data was 1.162 Å.31 The calculated values of the bending frequency, symmetric stretching frequency, and asymmetric stretching frequency of CO2 were 641 cm−1, 1332 cm−1, 2372 cm−1 and the experimental values were 667 cm−1, 1333 cm−1, 2349 cm−1, respectively. The good agreements between calculated results and the experimental data confirmed the validity of the present DFT calculations.
The CaO carbonation reaction and CaCO3 calcination reaction can be described by the unreacted-core model, which is also known as the shrinking-core model, where the reactions occur on heterogeneous surface.32,33 Hence, stable crystal surface which would be considered as reaction surface should be determined primarily. To compare the stability of various surfaces, the surface energy would be calculated first. For CaO and CaCO3, Esurf is calculated through eqn (5):
Esurf = [Eslab − Ebulk]/2A | (5) |
The energy values of (100), (110), and (111) surfaces of CaO crystal were calculated. The results were 0.795 J m−2, 1.419 J m−2, and 1.659 J m−2, respectively, so (100) surface was more stable and more easily obtained when CaO crystals were cleaved or in nature, being consistent with experimental data28 and ab initio calculated results.34 Meanwhile, the (110) surface of calcite crystal was calculated to be the most stable surface35 by DFT calculation. Therefore, next calculations would be performed on the (100) surface for CaO and (110) surface for CaCO3, respectively.
To simulate the reaction, an unit cell of CaO with a vacuum region of 15 Å was first used as the reactant. Different reaction sites were tested for CO2 on CaO (100) surface. Comparing the distances between C atom and three O atoms around it in the resulted structures with the central value of 1.29 Å of bulk carbonates,37 it was concluded that only a carbonate-like structure was formed and the carbonation reaction would not occur no matter how long the initial distance of C(CO2)–O(CaO) (R3) was. When R3 was larger than 5.0 Å, no structural change would happen during geometry optimization. When R3 was too short, a structure with a large imaginary frequency formed, in which R3 was prolonged to 1.307 Å, and the bond lengths of CO2 changed to 1.277 Å and 1.314 Å, respectively. Although the values were close to those of bulk carbonates, the atoms in the structure were disorder, as shown in Fig. 3(a), and the energy of the structure was too high. The conclusion was that a collapse of structure rather than a chemical reaction occurred. When R3 was larger than 1.0 Å, the CO2 molecule will be rejected or drown to keep R3 about 1.49 Å, which was almost equal to the sum of covalent radius of C and O, as shown in Fig. 3(b). In addition, the C–O lengths of CO2 molecule were about 1.24 Å, and the C–O–C angle of absorbed CO2 was 134.87°. The long C(CO2)–O(CaO) separation and relatively small increase in C–O bond lengths over the calculated gas-phase value of 1.175 Å indicated that the CO2 molecule physisorbed on the CaO (100) surface,38 and the adsorption energy was calculated to be only −48.10 kJ mol−1, which also confirmed the speculation. The electrons transfers were also calculated for comparison through Mulliken Population analysis, as shown in Fig. 4. The negative charge of O(CO2) was increased from −0.280 to −0.534, and for O(CaO) it decreased from −1.322 to −1.076. The electrons were found to transfer from O atom in CaO to C atom in CO2, and then to O atoms in CO2, the total electrons transferred to the adsorbed CO2 was −0.51. To compensate the charge transfer, tiny electrons transfer also occurred in other atoms.
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Fig. 3 Adsorption of CO2 on original unit cell CaO (100) surface (red ball: O atom, grey ball: C atom and green ball: Ca atom): (a) R3 = 0.8 Å (b) R3 = 1.2 Å. |
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Fig. 4 Mulliken Population analysis of atoms in single CO2 (upper left), CaO (100) (lower left) and adsorption structure (right) (red ball: O atom, grey ball: C atom and green ball: Ca atom). |
The surface chemistry of the cubic alkaline earth oxides (MgO, CaO, SrO, and BaO) is dominated by the Lewis basicity of surface oxide anions.39 This basicity increases along with the alkaline earth family as the metal ions become larger and more electropositive, and then become increasingly available for reaction.40 CO2 has been proved to physisorb on weak base MgO (100) surface, while the adsorption style of CO2 on CaO (100) surface is controversial. The results of the geometry of CO2 adsorption on CaO surface are discrepant. Schneider38 found that CO2 physisorbed on the weak base MgO surface and chemisorbed on the progressively more basic CaO through BaO surfaces, judged from the geometric parameters, i.e. r(Os–C) = 1.475 Å, r(C–O) = 1.250 Å, α(O–C–O) = 134.2° for MgO system and r(Os–C) = 1.384 Å, r(C–O) = 1.270 Å, α(O–C–O) = 129.1° for CaO system, and so on. Pacchioni40 calculated the geometries of CO2 on CaO (100) surface to be r(Os–C) = 1.376 Å, r(C–O) = 1.262 Å, α(O–C–O) = 130° and concluded that the CO2 reacted with CaO to form carbonate. Karlsen41 reported that CO2 was considerably distorted on CaO surface with the adsorption geometry of r(Os–C) = 1.49 Å, r(C–O) = 1.23 Å, α(O–C–O) = 134°. Kadossov42 obtained the bond length between the C atom in CO2 and O sites as 1.40–1.55 Å and the O–C–O angle of adsorbed CO2 as 130° and inferred the formation of carbonates. The above results in this work are not very satisfactory, so further work is needed to reveal the adsorption mode. The surface structure we used above might be too small to eliminate the interactions between CO2 and the periodic images of itself through destabilizing lateral steric repulsions, so thorough charge transfer during the absorption process would be suppressed. Then the surface structure was replaced by a 2 × 2 × 1 supercell of CaO (100) to eliminate the disturbance of the periodic images for further investigation, as shown in Fig. 5(a).
Different reaction sites were also tested for CaO (100) 2 × 2 × 1 structure. In all cases, the resulted bond length between the C atom in CO2 and O atom in CaO was about 1.39–1.42 Å, the bond length of C–O in adsorbed CO2 was prolonged to 1.26–1.27 Å, and the O–C–O angle of adsorbed CO2 was about 129°, while the dihedral angle of the four atoms was about 180°, as shown in Fig. 5(b) and (c). The adsorption energy obtained here was calculated to be about −150 kJ mol−1, being close to the experimental reaction heat of eqn (1), and the total electrons in the unit of CO2–O(CaO) was 1.595–1.634, being close to 1.536 of CO32− in calcite. All of these values indicated the occurrence of a chemical carbonation reaction.42
In the case of the unit cell structure, the periodic imaginary molecules interacted with each other and competed for electrons, it seemed like that the CaO was too little to contribute enough electrons for chemical reaction with CO2. In the carbonator, if CaO is not sufficient, a metastable carbonate-like state will form, which may decompose into CaO and CO2 before transported to the calciner, thus decreasing the capture efficiency. So it should be paid more attention that the CaO sorbent must be excess to ensure chemical reaction rather than physical absorption in the fluidized bed.
CO2 was found to be easily chemisorbed on CaO surface, resulting in the formation of carbonate. The carbonation reaction occurred as long as R3 was shorter than 5 Å, which was far longer than the sum of the covalent radius of C and O. The strong reactivity of the CaO surface against CO2 was in good agreement with experimental study.36 The adsorption configuration of CO2 was that the C atom adsorbed on O sites of CaO, and the O atoms in the adsorbed CO2 were oriented upward away from the surface. CO2 did not absorb either via the O atom or on Ca sites. A serial of reactions with different R3 value were calculated for comparison and R3 values were proved to have no influence on carbonation reaction. The reaction calculations were continued with R3 = 2.0 Å. Two initial CO2 orientations had been considered to further determine the favorable initial state of reaction, the linear CO2 molecule being parallel with the edge of surface (M1) or parallel with the diagonal of the surface (M2), as shown in Fig. 6(a) and (b). The resulted structures had no significant difference, which were also illustrated in Fig. 6(c) and (d). A detailed comparison involving structural parameters and Mulliken population analysis had been made in Table 1. It was found that the initial CO2 molecule orientation had no impaction on the carbonation reaction. So in the following TS searching calculations, there was no need to consider initial distance R3 or initial CO2 orientation, and an arbitrary initial state was adopted in the following calculations.
RC(CO2)–O(CaO) | RC–O | α(O–C–O) | ΔE | q(CO2) | q(CO3) | |
---|---|---|---|---|---|---|
M1 | 1.412 | 1.264 | 128.50° | −147.03 | −0.610 | −1.606 |
M2 | 1.393 | 1.266 | 129.38° | −147.46 | −0.634 | −1.595 |
To study the mechanism of the process of CO2 capture, the transition states of carbonation reaction had been analyzed. The results showed that there was no transition state during the process, and the energy of the systems decreased gradually. The activation energy of carbonation reaction was 0 kJ mol−1, being equal to experimental value.43 The zero activation energy indicated that carbonation reaction was a fast process and during the CO2 capture process, chemical reaction was not the rate determining step.
In the paper, the DFT methodology was applied to models of a “perfect” crystal of CaO. Then, the difference between calculated and experimental values might be due to the difference in the structures of calculated model and actual lime structure. In the process of CO2 adsorption on CaO, different O(CaO) environment gives different adsorption energy.44 It can be inferred reasonably that the experimental reaction heat value of −178 kJ mol−1 is a comprehensive result of reactions in many different chemical environments, as the structures of matters in nature are more complex and uncontrolled. In addition, due to the limitation of calculation, what we calculated were under 0 K, while the experimental values were measured under 298 K, so difference between calculated and experimental values to some extent might exist reasonably.
RC–O(1,2) | α(O1–C–O2) | Mulliken population analysis | |||||
---|---|---|---|---|---|---|---|
C | O1 | O2 | O3 | ||||
Reactant | 1.309 | 1.300 | 119.82 | 0.681 | −0.765 | −0.737 | −0.715 |
TS | 1.177 | 1.170 | 179.40 | 0.575 | −0.304 | −0.271 | −1.325 |
Product | 1.174 | 1.174 | 179.88 | 0.577 | −0.289 | −0.288 | −1.320 |
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Fig. 7 Calcination process of CaCO3 and structures of reactant (a), product (b), TS (c) (red ball: O atom, grey ball: C atom and green ball: Ca atom). |
For CaCO3 calcination, the reaction energy was larger than activation energy. So, in addition to break the C–O bond and optimize the structure of resulting CO2, more energy was needed to remove CO2 from CaCO3 surface. One conclusion could be made that calcination reaction mainly involved two processes: (1) chemical reaction: formation of CO2; (2) mass transfer: CO2 escaping from surface, which could be described by the following equations:
CaCO3 → CaO·CO2 | (6) |
CaO·CO2 → CaO + CO2 | (7) |
For the two processes, chemical reaction was the rate-limiting step. So increasing reaction temperature can be used to fasten reaction rate, thus improving reaction efficiency. In actual applications of fluidized bed, as the calcination process going on, more and more intermediate states (CaO·CO2) generate, so it should be ensured that the absorbed CO2 can be desorbed and then removed in due course to minimize the effect of the reverse reaction.
Carbonation of CaO and calcination of CaCO3 are reversible reactions, and the absolute reaction heat of them should be equal from theoretical point. But in this calculation, the difference between reaction heats of carbonation and calcination couldn't be ignored. A reasonable guess was made that the difference arises because of different chemical reaction environments, and different surface structures. Another set of calculations were done to confirm this guess. The reaction energies of single-molecule reactions were calculated, i.e., single CaO reacted with single CO2 and single CaCO3 decomposed, and the results were −268.40 kJ mol−1 and 265.78 kJ mol−1, respectively. The results suggested that chemical environments indeed played a role in the reactions. The CaCO3 crystal structure can promote calcination reaction, while amorphous CaO structure may be in favor of carbonation process, which can be an instructor in the design of CO2 capture fluidized bed.
In the process of calcination, chemical reaction was the rate-determining step, however, mass transfer also played a role. It could be speculated that for the carbonation process, which was the reverse reaction of calcination reaction, chemical reaction was rapid, and CO2 diffusion to CaO surface should be the critical stage. In practical cases, measurements to promote the contact between CO2 and CaO, such as increasing the surface area of CaO through reducing the particle size of CaO or preparing micro-hole CaO, can efficiently improve CO2 capture efficiency. Of course, enough CaO is also very important.
CO2 only showed physisorption on the unit cell of CaO (100) surface, due to competition for electrons transfer with its periodic imaginary molecules. Considering computation cost, a 2 × 2 × 1 supercell of CaO (100) surface was then employed, which was large enough to avoid the effect of periodic images. It was found that CO2 molecule reacted with surface O atom through C atom to form carbonate, and no reaction via O atom or on Ca atom was found. In the reaction between CaO and CO2, electrons transformed from surface O to C atom, and then to O atoms in CO2. To compensate the charge transfer, tiny electrons transfer from other atoms in the surface structure also occurred. Along with the electron transfer, C–O bonds in CO2 molecule were stretched to 1.26–1.27 Å and bent to a O–C–O angle of ∼129°, and the distance between C(CO2) and O(CaO) changed to 1.39–1.42 Å, leading to the formation of a new C–O bond. Through TS searching, the reaction energy and activation energy of carbonation process were calculated to be −147.64 kJ mol−1 and 0 kJ mol−1. The difference between calculated and experimental values might be due to the difference between model structure and actual CaO cleave surface structure, which needed further investigation. The zero activation energy indicated that chemical reaction was not the rate determining step during the CO2 capture process.
CaO is regenerated by calcination of CaCO3. The reaction energy of CaCO3 calcination was calculated to be 180.60 kJ mol−1, which was in good agreement with experimental values, 178 kJ mol−1. The TS structure of calcination process was CO2 physisorbing on CaCO3 surface with the activation energy of 166.85 kJ mol−1. The calcination reaction mainly involved chemical reaction process and mass transfer process, while the former one was the rate controlling step. In actual applications, it should be paid more attention to remove the product CO2 away to promote the calcination reaction.
Ea | Activation energy, kJ mol−1 |
ETS | Energy of transition state structure, kJ mol−1 |
ER | Energy of reactant structure, kJ mol−1 |
E | Reaction energy, kJ mol−1 |
EP | Energy of product structure, kJ mol−1 |
Eslab | Total energy of slab, J m−2 |
Esurf | Energy of surface, J m−2 |
Ebulk | Energy of bulk CaO or CaCO3 that has the same number of atoms with slab, J m−2 |
A | Surface area, m−2 |
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