Open Access Paper
26 September 2024 Investigate of mass transfer of CO2 absorption into the mixed solution of piperazine and diethanolamine in a packed column
Lei Peng, Qiang Fu, Zhi Li, Musong Lin, Yaohong Zhao, Zaikun Wu
Author Affiliations +
Proceedings Volume 13279, Fifth International Conference on Green Energy, Environment, and Sustainable Development (GEESD 2024) ; 132791U (2024) https://doi.org/10.1117/12.3044925
Event: Fifth International Conference on Green Energy, Environment, and Sustainable Development, 2024, Mianyang, China
Abstract
In our work, the aqueous solution of diethanolamine and piperazine was used to capture CO2 from a mixture of N2 and CO2 with a packed column. The effect of PZ/DEA mass ratio, gas flow rate, liquid flow rate, absorption temperature and CO2 content in the mixed gas on the overall volumetric mass transfer coefficient (KGaV) were discussed, respectively. The results showed that the value of KGaV increases with the increasing of PZ concentration, gas flow rate, liquid flow rate, respectively. However, KGaV value decreases as absorption temperature and the CO2 content of inlet gas increases. The results indicated that the addition of piperazine can effectively improve the mass transfer effect of CO2 absorption into DEA aqueous solution.

1.

INTRODUCTION

The widespread application of fossil fuels such as petroleum, natural gas, and coal is gradually increasing with the development of global industrialization1-3. This has caused lots of CO2 emission into the atmosphere in modern society. It is urgent to decrease the emission of CO2 owing to its contribution on global warming. Several technologies such as chemical absorption, adsorption and membrane separation are usually used to separate CO2 from mixed gas in chemical industry4-6. Among these technologies, the adsorption method has a series of advantages such as simple operation, easy control and low cost, but it also has drawbacks such as poor adsorption capacity and low selectivity7. Gas membrane separation technology has the advantages of low energy consumption, simple operation, and easy control. However, conventional membrane materials are limited by the upper limit of “Robeson”, making it difficult to obtain both high selectivity and high permeability8,9. Chemical absorption method has become the main method for carbon capture due to its good absorption capacity and rate. However, there are still some problems such as high energy consumption, severe material loss, and volatility. Hence, improving the existing absorption solution and developing new low energy CO2 absorbents have become a major direction for future solution absorption methods10-13.

Alcoholamine, as a commonly used CO2 absorbent, mainly includes N-methyldiethanolamine (MDEA), monoethanolamine (MEA), di-2-propanolamine (DIPA), diethanolamine (DEA) etc.14-17. Compared with other alcohol amines, although MEA has a high absorption rate, its high volatility and high energy consumption also affect its overall capture performance. Although DEA has a relatively low absorption rate, its low desorption temperature and high absorption capacity make it one of the main CO2 absorbents. If a certain accelerator is added to increase the absorption rate of DEA, it may greatly improve the CO2 absorption performance of DEA.

In recent years, piperazine (PZ) has been reported as an absorption promoter in the field of capturing CO2 18-20. It can be regarded that adding suitable piperazine to the alcohol amine will help improve the CO2 absorption rate. In our work, considering the shortcomings of DEA in absorption rate, a certain amount of piperazine was added in the preparation process of the absorbent to improve the absorption effect.

As the main gas absorption equipment, packed towers play a crucial role in the CO2 capture industry. Therefore, it is necessary to investigate the absorption performance of CO2 into the mixed solution of PZ and DEA with packed column. In our experiment, the mass transfer coefficient of CO2 into DEA solution activated by piperazine was calculated, and the effect of PZ on gas-liquid mass transfer was also discussed.

2.

THEORY

2.1

Reaction mechanism

Referred to References21-23, lots of reactions can take place as CO2 is absorbed by aqueous solution of piperazine and diethanolamine, as follows.

00067_PSISDG13279_132791U_page_2_1.jpg
00067_PSISDG13279_132791U_page_2_2.jpg
00067_PSISDG13279_132791U_page_2_3.jpg
00067_PSISDG13279_132791U_page_2_4.jpg
00067_PSISDG13279_132791U_page_2_5.jpg
00067_PSISDG13279_132791U_page_2_6.jpg
00067_PSISDG13279_132791U_page_2_7.jpg

The absorption mechanism of CO2 into the mixed solution includes two zwitterion mechanism: (1) the formation of zwitterion; (2) The base (DEA, PZ and PZCOO-) occurred PZ-monocarbamate, PZ-dicarbamate and protonated base in the deprotonation of the zwitterion24-26. The key deprotonation of the zwitterion in an aqueous blend of PZ and DEA mainly comes from DEA, PZ and a smaller amount of H2O. As usual, deprotonation is a rapid reaction as it only involves proton transfer, and the formation of zwitterion is considered a rate-controlled step. The addition of PZ helps to form more substrates, which is conducive to the formation of DEA zwitterions and thus facilitates absorption.

2.2

Absorption setup

As described in our previous work27, CO2 is absorbed by a packed column, and the gas-liquid reaction occurs at the packing surface in the column, as shown in Figure 1. The device mainly includes the parts: N2 cylinder, CO2 cylinder, buffer bottle, packed column, tank of absorbent recovery, rotameter, absorbent vessel, super constant temperature water bath, drying bottle and portable infrared gas analyzer.

Figure 1.

Absorption setup. (1): cylinder of N2 gas; (2): cylinder of CO2 gas; (3): buffer bottle; (4): packing column; (5): absorbent recovery tank; (6): temperature water bath; (7): constant flow pump; (8): absorbent vessel; (9): drying bottle; (10): infrared gas analyzer; (11)-(13): rotameters.

00067_PSISDG13279_132791U_page_3_1.jpg

At first, N2 and CO2 are mixed in a buffer bottle, and then enter the absorption tower. After CO2 is absorbed by the absorbent, the gas is discharged from the top of the packed column. After dried in a dryer, the CO2 content in the mixed gas is measured by a flue gas analyzer. The absorption temperature of gas and liquid is controlled by constant temperature water bath. The absorption experiment begins as the CO2 content in the inlet gas remains stable. At this moment, the CO2 content in the mixed gas is recorded, and the absorption liquid is pumped from the tank into the packed column.

Under normal circumstances, KG which means mass transfer coefficient was obtained by reaction kettle and wetted wall column that based on the theory of gas-liquid two films reported in some literatures28,29. In fact, this apparatus is just one unit of our packed column. In order to obtain the relationship between CO2 mass transfer and PZ concentration in industrial applications, the volumetric mass transfer coefficient (KGaV) of CO2 in packed tower absorption can be obtained according to equation (8)30-33.

00067_PSISDG13279_132791U_page_3_2.jpg

In the equation, G-inert gas flow rate (mol·m-2 ·s-1); P-operational pressure (Pa); aV-interfacial area per unit volume of packing (m2.m-3); yA-CO2 mole fraction in bulk; 00067_PSISDG13279_132791U_page_3_3.jpg equilibrium mole fraction at interface 00067_PSISDG13279_132791U_page_3_4.jpg.

3.

RESULT AND DISCUSSION

3.1

The relationship between PZ/DEA mass ratio and the value of KGaV

The CO2 absorption into the mixed solution of PZ and DEA was performed at the condition of 303 K absorption temperature, 200 mL.min-1N2 flow rate, 50 mL.min-1 CO2 flow rate and 2 rpm.min-1 constant flow pump. Four aqueous amine blends of DEA and PZ were used to absorb CO2 with 30 wt% total amine concentration, and the mass ratio of PZ/DEA were respectively 3/27, 6/24, 9/21, 12/18, the relation of KGaV values and PZ/DEA mass ratio was shown in Figure 2. Based on Equation (12). It is clear that the KGaV values increases with the increasing of PZ/DEA mass ratio. This is mainly due to the higher concentration of piperazine promoting the rate of diethanolamine formation into carbamate, which is beneficial for accelerating gas-liquid mass transfer.

Figure 2.

The relationship between PZ/DEA mass ratio and the value of KGaV.

00067_PSISDG13279_132791U_page_4_1.jpg

3.2

The relationship between temperature and the value of KGaV

The absorption of carbon dioxide by amine aqueous solution is a reversible reaction. Temperature is also a major factor affecting gas-liquid mass transfer. This article measured the total mass transfer coefficient of PZ-DEA aqueous solution absorbing CO2 at different ambient temperatures (operational conditions: 6/24 PZ/DEA mass ratio, 200 mL.min-1 N2 flow rate, 50 mL.min-1 N2 flow rate and 2 rpm.min-1 liquid constant flow pump), the result was shown in Figure 3. It shows that the KGaV value decreases with the increasing of absorption temperature as the other operational condition remains unchanged. This result just indicates that the absorption process is an exothermic reaction, which is consistent with the conclusion that the absorption of CO2 by alkanolamine is an exothermic process. Increasing the temperature is not conducive to absorption and mass transfer at 293-323 K, and 293 K is chosen as the optimal absorption temperature.

Figure 3.

The relationship between temperature and the value of KGaV.

00067_PSISDG13279_132791U_page_4_2.jpg

3.3

The relationship between liquid flow rate and KGaV value

In order to study the effect of CO2 absorbent flow rate, the KGaV values was determined as the rotation speed of constant pump increases from 0.5 rpm.min-1 to 2.0 rpm.min-1 (operational conditions: 6/24 PZ/DEA mass ratio, 303 K absorption temperature, 100 mL.min-1 N2 flow rate, 25 mL.min-1 N2 flow rate), the result was shown in Figure 4. It shows that KGaV values increases with the increasing of pump speed, which means increasing liquid flow rate is helpful to gas-liquid mass transfer. This is mainly because more liquid will facilitate the formation of more liquid films on the surface of the packing, thereby increasing the effective gas-liquid contact area and enhancing the mass transfer performance.

Figure 4.

The relationship between liquid flow rate and KGaV value.

00067_PSISDG13279_132791U_page_4_3.jpg

3.4

The relationship between gas flow rate and the value of KGaV

An appropriate gas flow rate is not only beneficial for improving mass transfer efficiency, but also for the smooth operation of the packed column. The KGaV values of CO2 into PZ-DEA solution were determined for different inlet gas flow in this experiment, the result was shown in Figure 5. It clearly indicates that increasing inlet gas flow can effectively improve the mass transfer coefficient. The results indicate that within a certain range of gas flow rate, increasing the gas flow rate is beneficial for full gas-liquid contact and improving mass transfer. Therefore, an appropriate liquid to gas ratio is a means to improve column efficiency.

Figure 5.

The relationship between gas flow rate and the value of KGaV.

00067_PSISDG13279_132791U_page_5_1.jpg

3.5

The relationship between CO2 content and the value of KGaV

The effect of CO2 Content in inlet gas on mass transfer of CO2 in the packed tower was measured within the range of 8% to 20%, the result was shown in Figure 6. From the figure, it can be seen that increasing the CO2 content in inlet gas on the contrary reduces the overall volumetric mass transfer coefficient, and high CO2 content is not conducive to CO2 mass transfer. This may be because a higher gas content will gradually reduce the effective components in the liquid of the packing section, reducing the mass transfer driving force. Therefore, it leads to an increasing of CO2 content in the exhaust gas and reduces mass transfer efficiency.

Figure 6.

The relationship between CO2 content and the value of KGaV.

00067_PSISDG13279_132791U_page_5_2.jpg

4.

CONCLUSION

The effect of PZ/DEA mass ratio, absorption temperature, absorbent flow rate, the CO2 content, gas flow rate on the overall volumetric mass transfer coefficient were investigated at normal pressure. It is observed that the performance of CO2 mass transfer in packed column significantly increases as PZ concentration increases. Piperazine has a certain promoting effect on the mass transfer of CO2 in solution. As the temperature of absorption increases, the decreasing of KGaV value prove that the absorption process is an exothermic reaction. The total volumetric mass transfer coefficient increases with the increasing of gas and liquid flow rates at the inlet, but decreases with the increasing of CO2 content in the inlet gas. Through the research in this article, it can conclude that improving existing alkanolamine absorbers and developing new composite absorbers will have a certain positive effect on improving CO2 capture performance. In the future, research on new absorbents will also be a major direction for CO2 capture using solution methods.

ACKNOWLEDGEMENTS

The authors are grateful for the financial support fromthe Open Project of hubei Key Laboratory of Industrial Fume & Dust Pollution Control (HBIK-2021-01), the Open Project of Key Laboratory of Novel Reactor and Chemical Technology of Hubei Province (NRG202105), Principal fund for Students of Wuhan Institute of Technology in China (XZJJ2020020) and the Training Program of College Students Innovation and Entrepreneurship in Hubei province (S202010490003, S202110490002).

REFERENCES

[1] 

Zhou, Y., Rao, Y. H., Wang, T. L. and Jens K. J., “Influence of formaldehyde on N-nitrosopiperazine formation from nitrite,” Int. J. Greenh. Gas. Con., 69 3 –40 (2018). https://doi.org/10.1016/j.ijggc.2017.12.013 Google Scholar

[2] 

Wang, T. L. and Jens, K. L., “Towards an understanding of the oxidative degradation pathways of AMP for postcombustion CO2 capture,” Int. J. Greenh. Gas. Con., 37 354 –361 (2015). https://doi.org/10.1016/j.ijggc.2015.03.017 Google Scholar

[3] 

Wu, Z. K., Huang, Z. L., Zhang, Y., Qin, Y. H., Ma, J. Y. and Luo, Y. B., “Kinetics analysis and regeneration performance of 1-butyl-3-methylimidazolium glycinate solutions for CO2 capture,” Chem. Eng. J., 295 64 –72 (2016). https://doi.org/10.1016/j.cej.2016.03.030 Google Scholar

[4] 

Liu, H. L., Xiao, M., Liang, Z. W. and Tontiwachwuthikul, P., “The analysis of solubility, absorption kinetics of CO2 absorption into aqueous 1-diethylamino-2-propanol solution,” AIChE Journal, 63 (7), 2694 –2704 (2017). https://doi.org/10.1002/aic.v63.7 Google Scholar

[5] 

Al-Janabi, N., Vakili, R., Kalumpasut, P., Gorgojo, P., Siperstein, F. R. and Fan, X. L., “Velocity Variation effect in fixed bed columns: a case study of CO2 capture using porous solid adsorbents,” AIChE Journal, 64 (6), 2189 –2197 (2018). https://doi.org/10.1002/aic.v64.6 Google Scholar

[6] 

Liu, H. L., “Investigation mechanism of DEA as an activator on aqueous MEA solution for postcombustion CO2 capture,” AIChE Journal, 64 (7), 2515 –2525 (2018). https://doi.org/10.1002/aic.v64.7 Google Scholar

[7] 

“Carbon Dioxide Capture and Storage,” IPCCCombriase, United Kingdom, (2005). Google Scholar

[8] 

Jiang, Z. Y., Chu, L. Y. and Wu, X. M., “Membrane-based separation technologies: from polymeric materials to novel process: an outlook from China,” Rev. Chem. Eng., 36 (1), 67 –105 (2019). https://doi.org/10.1515/revce-2017-0066 Google Scholar

[9] 

Ma, C. Y., Shukla, S. K., Samikannu, R., et al., “CO2 separation by a series of aqueous morpholinium-based ionic liquids with acetate anions,” ACS Sustainable Chem. Eng., 8 (1), 415 –426 (2020). https://doi.org/10.1021/acssuschemeng.9b05686 Google Scholar

[10] 

McCann, N., Maeder, M. and Attalla, M., “Simulation of enthalpy and capacity of CO2 absorption by aqueous amine system,” Ind. Eng. Chem. Res., 47 (6), 2002 –2009 (2008). https://doi.org/10.1021/ie070619a Google Scholar

[11] 

da Silva, E. F. and Svendsen, H. F., “Study of the carbamate stability of amines using ab initio methods and free-energy perturbations,” Ind. Eng. Chem. Res., 45 (8), 2497 –2504 (2006). https://doi.org/10.1021/ie050501z Google Scholar

[12] 

Alejandre, J., Rivera, J. L., Mora, M. A. and de La, G. V., “Force Field of Monoethanolamine,” J. Phys. Chem. B., 104 (6), 1332 –133 (2000). https://doi.org/10.1021/jp993101w Google Scholar

[13] 

Gutowski, K. E. and Maginn, E. J., “Amine-functionalized task-specific ionic liquids: a mechanistic explanation for the dramatic increase in viscosity upon complexation with CO2 from Molecular simulation,” J. Am. Soc., 130 (44), 14690 –14704 (2008). https://doi.org/10.1021/ja804654b Google Scholar

[14] 

Rangwala, H. A., Morrell, B. R., Mather, A. E. and Otto, F. D., “Absorption of CO2 into aqueous tertiary amine/MEA solutions,” Can. J. Chem. Eng., 70 482 –490 (1992). https://doi.org/10.1002/cjce.v70:3 Google Scholar

[15] 

Rinker, E. B., Ashour, S. S. and Sandall, O. C., “Absorption of carbon dioxide into aqueous blends of diethanolamine and methyldiethanolamine,” Ind. Eng. Chem. Res., 39 4346 –4356 (2000). https://doi.org/10.1021/ie990850r Google Scholar

[16] 

Furhacker, M., Pressl, A. and Allabashi, R., “Aerobic biodegradability of methyldiethan-olamine (MDEA) used in natural gas sweetening plants in batch tests and continuous flow experiments,” Chemosphere, 52 1743 –1748 (2003). https://doi.org/10.1016/S0045-6535(03)00371-0 Google Scholar

[17] 

DeMontigny, D., Tontiwachwuthikul, P. and Chakma, A., “Comparing the absorption performance of packed columns and membrane contactors,” Ind. Eng. Chem. Res., 44 5726 –5732 (2005). https://doi.org/10.1021/ie040264k Google Scholar

[18] 

Das, B., Guo, H. J., Xiong, L., et al., “Piperazine-activated diethanolamine formulation for post-combustion CO2 capture,” J. Ind. Eng. Chem., 118 519 –532 (2023). https://doi.org/10.1016/j.jiec.2022.11.035 Google Scholar

[19] 

Khan, A. A., Halder, G. N. and Saha, A. K., “Experimental investigation of sorption characteristics of capturing carbon dioxide into piperazine activated aqueous2-amino-2-methyl-1-propanol solution in a packed column,” Int. J. Greenh. Gas. Con., 44 217 –226 (2016). https://doi.org/10.1016/j.ijggc.2015.11.020 Google Scholar

[20] 

Zhao, B. T., Fang, T. B., Qian, W. F., Liu, J. P. and Su, Y. X., “Process simulation, optimization and assessment of post-combustion carbon dioxide capture with piperazine-activated blended absorbents,” J. Clean. Prod., 282 124502 (2021). https://doi.org/10.1016/j.jclepro.2020.124502 Google Scholar

[21] 

Dash, S. K., Samanta, A. K., Samanta, A. N. and Bandyopadhyay, S. S., “Absorption of carbon dioxide in piperazine activated concentrated aqueous 2-amino-2-methyl-1-propanol solvent,” Chem. Eng. Sci., 66 3223 –3233 (2011). https://doi.org/10.1016/j.ces.2011.02.028 Google Scholar

[22] 

Zhang, T. T., Yu, Y. S. and Zhang, Z. X., “An interactive chemical enhancement of CO2 capture in the MEA/PZ/AMP/DEA binary solutions,” Int. J. Greenh. Gas. Con., 74 119 –129 (2018). https://doi.org/10.1016/j.ijggc.2018.04.023 Google Scholar

[23] 

Chen, Z. B., Jing, G. H., Lv, B. H. and Zhou, Z. M., “An efficient solid-liquid biphasic solvent for CO2 capture: crystalline powder product and low heat duty,” ACS Sustainable Chem. Eng., 8 14493 –14503 (2020). https://doi.org/10.1021/acssuschemeng.0c04616 Google Scholar

[24] 

Bishnoi, S. and Rochelle, G. T., “Absorption of carbon dioxide into aqueous piperazine: reaction kinetics, mass transfer and solubility,” Chem. Eng. Sci., 55 5531 –5543 (2000). https://doi.org/10.1016/S0009-2509(00)00182-2 Google Scholar

[25] 

Derks, P. W. J., Kleingeld, C., Van Aken, C., Hogendoorn, J. A. and Versteeg, G. F., “Kinetics of absorption of carbon dioxide in aqueous piperazine solutions,” Chem. Eng. Sci., 61 6837 –6854 (2006). https://doi.org/10.1016/j.ces.2006.07.009 Google Scholar

[26] 

Samanta, A. and Bandyopadhyay, S. S., “Kinetics and modeling of carbon dioxide adsorption into aqueous solutions of piperazine,” Chem. Eng. Sci., 62 7312 –7319 (2007). https://doi.org/10.1016/j.ces.2007.08.022 Google Scholar

[27] 

Huang, Z. L., Deng, Z. Y., Ma, J. Y., Qin, Y. H., Zhang, Y., Luo, Y. B. and Wu, Z. K., “Comparison of mass transfer coefficients and desorption rates of CO2 absorption into aqueous MEA+ionic liquids solution,” Chem. Eng. Res. Des., 117 66 –72 (2017). https://doi.org/10.1016/j.cherd.2016.10.012 Google Scholar

[28] 

Dugas, R. E. and Rochelle, G. T., “CO2 absorption rate into concentrated aqueous monoethanolamine,” Chem. Eng. Data, 56 2187 –2195 (2011). https://doi.org/10.1021/je101234t Google Scholar

[29] 

Puxty, G., Rowland, R. and Attalla, M., “Comparison of the rate of CO2 absorption into aqueous ammonia,” Chem. Eng. Sci., 65 915 –922 (2010). https://doi.org/10.1016/j.ces.2009.09.042 Google Scholar

[30] 

Frimpong, R. A., Johnson, D., Richburg, L., Hogston, B., Remias, J. E., Neathery, J. K. and Liu, K. L., “Comparison of solvent performance for CO2 capture from coal-derived flue gas: apilot scale study,” Chem. Eng. Res. Des., 91 963 –969 (2013). https://doi.org/10.1016/j.cherd.2012.10.006 Google Scholar

[31] 

Demontigny, D., Tontiwachwuthikul, P. and Chakma, A., “Parametric studies of carbon dioxide absorption into highlyconcentrated monoethanolamine solutions,” Can. Chem. Eng., 79 137 –142 (2001). https://doi.org/10.1002/cjce.v79:1 Google Scholar

[32] 

Tontiwachwuthikul, P., Meisen, A. and Lim, C. J., “CO2 absorption by NaOH, monoethanolamine and 2-amino- 2-methyl-1-propanol solutions in a packed column,” Chem. Eng. Sci., 47 381 –390 (1992). https://doi.org/10.1016/0009-2509(92)80028-B Google Scholar

[33] 

Frimpong, R. A., Johnson, D., Richburg, L., Hogston, B., Remias, J. E., Neathery, J. K. and Liu, K. L., “Comparison of solvent performance for CO2 capture from coal-derived flue gas: apilot scale study,” Chem. Eng. Res. Des., 91 963 –969 (2013). https://doi.org/10.1016/j.cherd.2012.10.006 Google Scholar
(2024) Published by SPIE. Downloading of the abstract is permitted for personal use only.
Lei Peng, Qiang Fu, Zhi Li, Musong Lin, Yaohong Zhao, and Zaikun Wu "Investigate of mass transfer of CO2 absorption into the mixed solution of piperazine and diethanolamine in a packed column", Proc. SPIE 13279, Fifth International Conference on Green Energy, Environment, and Sustainable Development (GEESD 2024) , 132791U (26 September 2024); https://doi.org/10.1117/12.3044925
Advertisement
Advertisement
RIGHTS & PERMISSIONS
Get copyright permission  Get copyright permission on Copyright Marketplace
KEYWORDS
Carbon monoxide

Absorption

Liquids

Carbon dioxide

Adsorption

Industrial chemicals

Industrial applications

Back to Top