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Analysis of the K2CO3-NH3 Solvent Properties for Carbon Capture Applications

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Analysis of the K

2

CO

3

-NH

3

solvent properties for carbon capture applications

Stefano Lillia1 Davide Bonalumi1 Philip Fosbøl2 Kay Thomsen2 Gianluca Valenti1 Indira Jayaweera3

1Politecnico di Milano – Dipartimento di Energia, Via R. Lambruschini 4, Milano, Italy 2Technical University of Denmark, Department of Chemical Engineering, Center for Energy

Resource Engineering, Søltofts Plads, 2800, Kgs. Lyngby, Denmark

3SRI International, 333 Ravenswood Avenue, Menlo Park, CA 94025, USA

Abstract

Absorption-based systems that typically employ amines such as monoethanolamine (MEA) are in commercial use for scrubbing CO2 from industrial flue and process gases. However, many challenges

must be overcome when applying amine-based technology for the treatment of pulverized coal-fired power plants such as toxicity, degradation, high energy consumption associated with regeneration of the solvent, low regeneration pressure and cost of the chemicals. Other solvents such as aqueous solutions of ammonia (NH3) (Chilled Ammonia Process) and aqueous solution of potassium

carbonate (K2CO3) are mature non-amine alternatives to the state-of-the-art MEA technology.

Technology based on NH3 is capable of capturing CO2 at high loadings compared with MEA-based

technology. In addition, NH3-based technology can strip CO2 at high pressure, thereby reducing CO2

compression costs and it has a kinetic of absorption comparable to the amine technologies at temperatures around 25°C. However, this process requires gas washing to reduce the NH3 emissions

in the scrubbed flue gas [1-2]. The K2CO3-based process has lower regeneration energy requirements

and no emission issues. However, it has a low kinetic of absorption, a very low loading capacity, and low-pressure of CO2 regeneration. Both the solvents (NH3 and K2CO3) have no problems of

degradation and toxicity and they have low costs compared to the amines [3].

The aim of this work is the study of the thermodynamic properties and the kinetic of absorption of the mixture between the NH3 and K2CO3 in the same solvent in order to investigate a solution with

low heat duty of regeneration reducing the ammonia slip and maintaining a higher regeneration pressure [4].

The novelty is the analysis of the thermodynamic and the kinetic of absorption of the Mixed-salt Technology solvent for the carbon capture application applied on the pulverized coal-fired exhausts with 13% of CO2 concentration. The thermodynamic analysis of the properties is conducted with the

Extended UNIQUAC thermodynamic model proposed by Thomsen and Rasmussen [5] in its new version calibrated with both the experimental data of the ternary systems NH3-CO2-H2O and K2CO3

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Thermodynamic Analysis

Because of primary importance, the heat of CO2 desorption is evaluated as a function of (i) the

capacity of the solvent (sum of the NH3 and K2CO3 molality) and (ii) the composition of the NH3 and

K2CO3 in the solvent. Figure 1 shows the trend of the heat of CO2 desorption as a function of the cited

parameters. The curves are drawn for a range of composition where the salts do not precipitate, since the salt precipitation does not allow the use of the packed column for the CO2 absorption. The chart

highlights that the solvent with only K2CO3 has a heat of desorption lower than all the solvents with

NH3 and K2CO3. Moreover, when the iso-capacity reaches an amount of K2CO3 around 1 [mol/kgH2O],

the hHeat duty decreases with the increment of the concentration of K2CO3. The most promising

iso-capacity is iso-cap 4 molal since the NH3 and K2CO3 are not too much diluted and the salt

precipitation is not an issue for a wide range of composition between NH3 and K2CO3.

Figure 1. The chart presents the heat of CO2 absorption at 120°C as a function of the solvent composition at different values of

iso-capacity. The curves are interrupted when the salts deposition occurs.

A second property evaluated is the partial pressure of NH3 at the absorption pressure in order to

study the impact of the K2CO3 on the ammonia slips. Figure 2 (Left) shows the partial pressure of

ammonia at constant CO2 partial pressure (0.013) and at varying initial ammonia concentration at

25 °C as a function of the K2CO3 content. Figure 2 (Right) depicts the concentration of species for

the solvent with an initial concentration of 4 molal ammonia as a function of the K2CO3 content in

the solvent. The results do not show a significant variation of the ammonia partial pressure with rising K2CO3 fraction. Indeed, as described by the speciation chart, the free ammonia in the liquid

phase, NH3(aq), is almost constant with varying K2CO3 content. This fact is a benefit for the solvent

as the ammonia slip remains constant while increasing the capacity of the solvent.

0 10 20 30 40 50 60 70 80 0 1 2 3 H ab s (k J/m o lCO2 )

molality of K2CO3[mol/kgH2O]

iso-cap. 10 iso-cap. 8 iso-cap. 6 iso-cap. 4 K2CO3 solution 120°C

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Figure 2. (Left) Ammonia partial pressure as a function of the K2CO3 concentration for different ammonia initial concentration. The

partial pressure of CO2 is constant, 0.013 bar, and the temperature is 25 °C. (Right) Molality of every species in the solvent for a

solvent with an initial ammonia molality of 4. In both charts the lines are interrupted when salt precipitation starts.

Rate of CO2 absorption measurement with the Wetted Wall Column

After the thermodynamic analysis the iso-capacity of 4 molal is selected as the most promising for a carbon capture application. For this case the overall mass transfer coefficient of the CO2 𝐾𝑜𝑣 is

measured experimentally with the Wetted Wall Column apparatus. The overall mass transfer coefficient 𝐾𝑜𝑣 [mol/(Pa m2 s)] is defined as

𝜑𝐶𝑂2 = 𝐾𝑜𝑣(𝑃𝐶𝑂 2 𝑔𝑎𝑠 −𝑃𝐶𝑂 2 𝑙𝑖𝑞) (1) where 𝜑𝐶𝑂2 [mol/(m

2 s)] is the surface flux of CO

2 absorbed by the solvent, 𝑃𝐶𝑂𝑔𝑎𝑠2 [Pa] is the partial

pressure of CO2 in the gas phase and is the pressure of CO2 in the liquid phase.

The aim is the comparison of the rate of the absorption for different composition of the solvent with the same CO2 capacity at different temperatures and two different CO2 loadings, a RICH and a LEAN

case, which are the solvent conditions at the top and at the bottom of the absorber column. The results in Figure 3 (Left) shows that the kinetic of absorption decrease when the K2CO3 concentration

increase with respect of the ammonia. Indeed, as demonstrated by Lillia et al. [6], the faster reaction is between ammonia and CO2. Rising the K2CO3 concentration, the free ammonia concentration

decreases and consequently decreases also the rate of absorption. This correlation is highlighted in Figure 3 (Right) where the chart overlay the values of the 𝐾𝑜𝑣 (left y-axis) with the concentration of

the free ammonia in the bulk phase calculated with the Extended UNIQUAC model (right y-axis). Finaly, comparing the overall mass transfer coefficient of the analysed cases with data in literature measured for the solvent with pure K2CO3, NH3 enhance the overall mass transfer coefficient almost

3 times [7]. 0 0.01 0.02 0.03 0.04 0.05 0 1 2 3 4 NH 3 pa rt ial pr ess ur e [ba r]

molality of K2CO3[mol/kgH2O]

4 mol NH3 8 mol NH3 2 mol NH3 6 mol NH3 0 0.5 1 1.5 2 2.5 3 0 1 2 3 4 m o lal it y o f t he sp ec ie [ m o l/k gH2 O ]

molality of K2CO3[mol/kgH2O]

NH4+ HCO3-

NH2COO-NH3(aq)

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Figure 3. Left: overall mass transfer coefficient as a function of the K2CO3 initial molality for the iso-capacity of 4 molal at three

different temperatures (25°C, 35°C and 45°C) and for two different CO2 loadings (RICH loading and LEAN loading). Right: on the

left y-axis the overall mass transfer coefficient is represented as a function of the K2CO3 initial molality for the iso-capacity of 4 molal

at 35°C and for two different CO2 loadings (RICH loading and LEAN loading), while on the right y-axis the free ammonia molality of

the bulk solution calculated with the Extended UNIQUAC is represented as a function of the K2CO3 initial molality for the iso-capacity

of 4 molal at 35°C and for two different CO2 loadings (RICH loading and LEAN loading.

Concluding, the K2CO3 reduces the ammonia slip with reduction of the CO2 heat of desorption of the

CO2 during the regeneration of the solvent. Comparing to K2CO3 solvent the ammonia enhances the

rate of absorption of the solvent reducing the surface needed for the CO2 capture.

Bibliography

[1] G. Valenti, D. Bonalumi, and E. Macchi, “Modeling of ultra super critical power plants integrated with the chilled ammonia process,” Energy Procedia, vol. 4, pp. 1721–1728, 2011. [2] H. Jilvero, F. Normann, K. Andersson, and F. Johnsson, “The rate of CO2 absorption in

ammonia-implications on absorber design,” Ind. Eng. Chem. Res., vol. 53, no. 16, pp. 6750– 6758, Apr. 2014.

[3] K. A. Mumford et al., “Post-combustion capture of CO 2: Results from the solvent absorption capture plant at hazelwood power station using potassium carbonate solvent,”

Energy and Fuels, vol. 26, no. 1, pp. 138–146, 2012.

[4] I. Jayaweera, P. Jayaweera, R. Elmore, J. Bao, and S. Bhamidi, “Update on mixed-salt technology development for CO2 capture from post-combustion power stations,” Energy

Procedia, vol. 63, pp. 640–650, 2014.

[5] K. Thomsen and P. Rasmussen, “Modeling of vapor–liquid–solid equilibrium in gas–aqueous electrolyte systems,” Chem. Eng. Sci., vol. 54, no. 12, pp. 1787–1802, Jun. 1999.

[6] S. Lillia, D. Bonalumi, P. L. Fosbøl, K. Thomsen, and G. Valenti, “Experimental study of the aqueous CO2-NH3 rate of reaction for temperatures from 15 °C to 35 °C, NH3concentrations from 5% to 15% and CO2loadings from 0.2 to 0.6,” Int. J. Greenh. Gas Control, vol. 70, no. July 2017, pp. 117–127, 2018.

[7] A. Gladis, M. T. Gundersen, P. L. Fosbøl, J. M. Woodley, and N. von Solms, “Influence of temperature and solvent concentration on the kinetics of the enzyme carbonic anhydrase in carbon capture technology,” Chem. Eng. J., vol. 309, pp. 772–786, 2017.

0.0E+00 1.0E-07 2.0E-07 3.0E-07 4.0E-07 5.0E-07 6.0E-07 7.0E-07 8.0E-07 9.0E-07 1.0E-06 0 1 2 3 Kov [ m o l/(Pa m 2s) ]

molality of K2CO3[mol/kgH2O]

LEAN;25°C RICH;25°C LEAN;35°C RICH;35°C LEAN;45°C RICH;45°C 0 0.2 0.4 0.6 0.8 1 1.2 1.4 1.6 0.0E+00 1.0E-07 2.0E-07 3.0E-07 4.0E-07 5.0E-07 6.0E-07 7.0E-07 8.0E-07 0 1 2 3 NH 3 (aq ) m o lal it y [m o l/k gH2 O ] Kov [ m o l/(Pa m 2s) ]

molality of K2CO3[mol/kgH2O]

Kov LEAN 35°C Kov RICH 35°C NH3(aq) LEAN 35°C NH3(aq) RICH 35°C

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