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Scientific Review
ISSN(e): 2412-2599, ISSN(p): 2413-8835
Vol. 3, No. 5, pp: 43-53, 2017
URL: http://arpgweb.com/?ic=journal&journal=10&info=aims
43
Academic Research Publishing Group
Absorption Rate of Carbon Dioxide from Gas Mixture
Jafar Ghani Majeed Department of Materials Engineering, College of Engineering, Al-Mustansiriyah University, Baghdad,
Iraq
1. Introduction
Carbon dioxide is one of the more frequent found gases on the earth. It is a main product in combustion
processes and the natural metabolism of living organisms. Carbon dioxide discharged by the consumption of fossil
fuel for power and heat production is said to occupy nearly 35- 40 % of the amount of discharged CO2 all over the
world [1-3]. Environmental issues caused by exhaust greenhouse gases (GHG) and toxics have become global
problems. Through the past studies of five decades, increased GHG levels in atmosphere is believed to cause global
warming, in which CO2 is the largest contributors. International Panel on Climate Change (IPCC) predicts that the
CO2 content in atmosphere may contain up to 570 ppm CO2, causing an increase in mean global temperature around
1.9℃ and an increase mean sea level of 38 m [4]. Also accompanied is species extinction.
Indoor CO2 levels usually vary between 400 and 2000 ppm (parts per million). Outdoor CO2 levels are usually
350 - 450 ppm. Heavily industrialized or contaminated areas may periodically have a CO2 concentration of up to 800
ppm. The levels of outdoor CO2 are higher in areas where traffic is very heavy.
CO2 must not be confused with carbon monoxide (CO), a very toxic gas that is a by-product from poor
combustion in i.e. cars and fireplaces. Carbon monoxide is dangerous at very low concentrations (25 to 50 ppm). In
industrial environments where process generated CO2 dominates (or CO2 not generated by people), for example in
breweries, packaging industry, freezer storages etc, the maximum Permitted CO2 concentration according to most
standards is as high as 5000 ppm during an 8-hour working period. You will not find such high levels in a home or
in an office environment where people are the main source of carbon dioxide.
Several methods have been proposed to remove CO2 from the air, or from flue gases, such as chemical
absorption, physical absorption, membrane separation, biochemical methods, and the catalytic conversion method. In
addition to these methods, the absorption of carbon dioxide in an alkaline solution with crystallization has also been
adopted to explore the removal of carbon dioxide from waste gas [5]. These usually involve using a variant of the
Kraft process. Scrubbing processes may be based on sodium hydroxide [6-8]. The CO2 is absorbed into solution,
transferred to lime via a process called causticization and released in a kiln.
Some researchers outlined a specific methods of air capture [9-13]. CO2 is absorbed by an alkaline NaOH
solution to produce dissolved sodium carbonate. The absorption reaction is a gas liquid reaction, strongly
exothermic, (below):
2NaOH (aq) + CO2 (g) → Na2CO3 (aq) + H2O (1)
The mechanism of reaction between the acidic oxide and the alkali depends on the concentration of the alkali
solution.
Abstract: Absorption of CO2 gas from CO2/Air mixture into aqueous sodium hydroxide solution has been
achieved using packed column in pilot scale at constant temperature (T) of 25±1℃.The aim of the present work
was to improve the Absorption rate of this process, to find the optimal operation conditions, and to contribute to
the using of this process in the chemical industry. Absorption rate (RA) was measured by using different
operating parameters: gas mixture flow rate (G) of 360-540 m3/h, carbon dioxide inlet concentration (CCO2) of
0.1-0.5 vol. %, NaOH solution concentration (CNaOH) of 1-2 M, and liquid holdup in the column (VL) of 0.022-
0.028 m3 according to experimental design. The measured RA was in the range of RA = 3.235 – 22.340 k-mol/h.
Computer program (Statgraphics/Experimental Design) was used to estimate the fitted linear model of RA in
terms of (G, CCO2, CNaOH, and VL), and the economic aspects of the process. R-squared of RA model was
91.7659 percent, while the standard error of the estimate shows the standard deviation of the residuals to be
1.7619. The linear model of RA was adequate, the operating parameters were significant except the liquid holdup
was not significant, and the interactions were negligible.
Keywords: Packed column; CO2 absorption; NaOH solution; Absorption rate.
Scientific Review, 2017, 3(5): 43-53
44
(a) When the alkali (NaOH) solution is very dilute (pH < 8), carbon dioxide first reacts with water to form carbonic
acid (H2CO3) slowly. The acid thus formed then reacts with the alkali to give sodium hydrogen carbonate
(NaHCO3):
CO2 (g) + H2O (l) ↔ H2CO3 (aq) (2)
NaOH (aq) + H2CO3 (aq) → NaHCO3 (aq) + H2O (l) (3)
(b) When the alkali solution is a fairly concentrated one (pH > 10), carbon dioxide directly reacts with it to form the
bicarbonate, which further reacts with the alkali to form sodium carbonate (Na2CO3) as the main product by
complete neutralization:
NaOH (aq) + CO2 (g) → NaHCO3 (aq) (4)
NaHCO3 (aq) + NaOH (aq) → Na2CO3 (aq) + H2O (l) (5)
Thus, only when the concentration of the alkali solution is quite low, the reaction proceeds via the formation of
carbonic acid. But the acidic oxide is not completely neutralized in this case.
2. Experimental Work
2.1. Experimental Apparatuses
The main equipment of the experimental apparatus as shown in Figure 1 is the packed column (1), with the size
of 2 m height and 0.2 m diameter. The main complementary apparatus and pipe lines are as follows: Compressed air
(2), carbon dioxide gas (3), flow meter for compressed air (4), flow meter for CO2 gas (5) , mixing gas chamber (6),
gas mixture vent (7), thermostat (8), gas mixture into packed column (9), temperature indicator (10), pH indicator
(11), gas mixture to CO2 analyzer (12), CO2 analyzer (13), gas vent (14), gas mixture out (15), flow meter for
aqueous NaOH solution (16), head tank (17), outlet gas mixture to CO2 gas analyzer (18), aqueous sodium
hydroxide solution into packed column (19), product tank (20), aqueous sodium hydroxide solution feed tank (21),
feed pump (22), thermostat (23).
Figure-1. Schematic diagram of the experimental apparatus for CO2 gas absorption from CO2/Air gas mixture into aqueous NaOH solution in
packed column.
20
19
23
22
21
M 17
16
15
18
14
12
13
7
2
3
6
4
5
8
10 11
9
1
Scientific Review, 2017, 3(5): 43-53
45
2.2. Operating Parameters
The preliminary experiments were carried out to absorb of CO2 gas from gas mixture into aqueous NaOH
solution in pilot scale packed column using experimental apparatus as shown in Figure 1 to find the proper operating
parameters would be used in this work. Operating variable parameters were as follows:
* Gas mixture flow rate (G): 360-540 m3
/h.
* CO2 gas inlet concentration (CCO2): 0.1-0.5 vol. %.
* Aqueous NaOH solution concentration (CNaOH): 1-2 M.
* Liquid temperature (T): 25±1℃.
* Liquid holdup in the column (VL): 0.022-0.028 m3
.
2.3. Absorption of CO2 from CO2/Air Gas Mixture
Experiments of absorption of CO2 gas from CO2/Air gas mixture into aqueous NaOH solution have been
carried out using the mentioned various operating parameters by using experimental apparatus as shown in Figure 1,
according to experimental design plan seen in Table 1. The flow rates of compressed air (2) and CO2 gas (3) from
gas cylinder were measured by flow meters (4) and (5) respectively, and enter the mixing chamber (6). The gas
mixture (9) enters the packed column (1) through the thermostat (8) from lower part. The gas mixture via the gas line
(12) enters CO2 gas analyzer (13) to measure CO2 inlet concentration in the gas mixture. Aqueous NaOH solution
from NaOH solution feed tank (21) by feed pump (22) enters the upper part of the column through the liquid feeding
line (19). The thermostat (23) is maintained the desired liquid temperature constant in packed column (1) during the
all experiments runs. One part of gas mixture from the top of column through the gas mixture line (18) was taken
into CO2 gas analyzer (13) to measure outlet CO2 gas concentration, while the other part of gas mixture discharge to
atmosphere via the gas mixture line (15). In the column, the liquid temperature measured by temperature gage (10),
while the pH of the liquid is measured by digital pH-meter (11). The resultant reaction product Na2CO3 solution from
downer part of column sent to solution product tank (20).
Table-1. Experimental design plan for absorption of CO2 into aqueous NaOH solution.
Liquid holdup in
the column
(VL)
NaOH solution
concentration
(CNaOH)
CO2 gas inlet
concentration
(CCO2)
Gas mixture flow
rate
(G)
Run No.
(m3
)(M)(vol. %)(m3
/h)
0.0251.50.34501
0.02220.55402
0.02810.53603
0.02210.13604
0.02220.53605
0.02820.55406
0.02810.13607
0.0251.50.34508
0.02820.13609
0.0251.50.345010
0.02220.136011
0.02810.154012
0.02820.536013
0.02210.536014
0.02220.154015
0.02210.554016
0.02210.154017
0.02820.154018
0.02810.554019
2.4. Definition of CO2 Absorption Rate
The CO2 inlet flow rate (Gin) is calculated using the following equation:
Gin = [(Qair x Dair /Mair)/ (1 –YCO2, in)] YCO2, in (6)
Where,
Gin = CO2 inlet flow rate, k-mol/h.
Scientific Review, 2017, 3(5): 43-53
46
Qair =Air volumetric flow rate, m3
/h.
Dair = Density of air, kg/m3
at standard conditions.
Mair = Molecular weight of air, kg/k-mol.
YCO2, in = CO2 mole fraction at inlet of packed column, vol. %.
The CO2 outlet flow rate (Gout) is calculated using the following equation:
Gout = [(Qair xDair/Mair)/ (1-YCO2, out)]YCO2, out (7)
Where,
Gout = CO2 outlet flow rate, k-mol/h.
YCO2, out = CO2 mole fraction at outlet of packed column, vol. %.
The CO2 absorption rate (RA) is the difference between the inlet and outlet CO2 flow rates [14 -17]:
RA = Gin – Gout (8)
Where,
RA = CO2 absorption rate, k-mol/h.
3. Results and Discussion
3.1. Absorption Rate Calculation
The absorption of CO2 gas from CO2/Air gas mixture into aqueous sodium hydroxide (NaOH) solution were
carried out according to experimental design plan in Table 1 with the variation of gas mixture flow rate (G), CO2 gas
inlet concentration (CCO2), , aqueous NaOH solution concentration (CNaOH), and liquid holdup in the column (VL).
Absorption rate (RA) was calculated by using equation (4). The RA of CO2 gas from gas mixture CO2/Air was in
the range of RA = 3.235 – 22.340 k-mol/h. The results of RA are summarized in Table 2:
Table-2. Data base of experimental design and results of CO2 gas absorption from gas mixture CO2 /Air into aqueous NaOH solution.
Absorptio
n rate
(RA)
Liquid holdup in
the column
(VL)
NaOH solution
concentration
(CNaOH)
CO2 gas inlet
concentration
(CCO2)
Gas mixture
flow rate
(G)
Run
No.
(k-mol/h)(m3
)(M)(vol. %)(m3
/h)
12.3500.0251.50.34501
21.2040.02220.55402
14.2600.02810.53603
3.2350.02210.13604
16.6160.02220.53605
22.3400.02820.55406
7.5430.02810.13607
13.5640.0251.50.34508
10.4540.02820.13609
11.8950.0251.50.345010
7.4300.02220.136011
5.5500.02810.154012
14.6500.02820.536013
13.4140.02210.536014
9.4500.02220.154015
18.7310.02210.554016
7.3080.02210.154017
11.3680.02820.154018
20.5150.02810.554019
Scientific Review, 2017, 3(5): 43-53
47
The effects of operating parameters on absorption rate of CO2 gas from CO2/Air gas mixture could be seen
as in the following Figures:
Figure-2. Effect of CO2 gas inlet concentration, and gas mixture flow rate on Absorption rate of CO2 gas from CO2/Air mixture.
Figure-3. Effect of NaOH concentration, and gas mixture flow rate on Absorption rate of CO2 gas from CO2/Air mixture.
Scientific Review, 2017, 3(5): 43-53
48
Figure-4. Effect of liquid holdup,, and gas mixture flow rate on Absorption rate of CO2 gas from CO2/Air mixture.
Figure-5. Effect of aqueous NaOH concentration, and CO2 inlet concentration on Absorption rate of CO2 gas from CO2/Air mixture.
Figure-6. Effect of aqueous NaOH concentration, and liquid holdup on Absorption rate of CO2 gas from CO2/Air mixture.
Scientific Review, 2017, 3(5): 43-53
49
Figure-7. Effect of CO2 inlet concentration, and liquid holdup on Absorption rate of CO2 gas from CO2/Air mixture.
The 3 D sequential Graphs/Box plot and Block plot for Absorption rate (RA) with independent parameters: gas
mixture flow rate (G), inlet CO2 gas concentration (CCO2), aqueous NaOH solution (CNaOH), and liquid holdup (VL)
as in the following figures:
Figure-8. 3 D sequential Graph/Box plot for Absorption rate of CO2 gas from CO2/Air mixture with operating parameters.
Scientific Review, 2017, 3(5): 43-53
50
Figure-9. 3 D sequential Graph/Block plot for Absorption rate of CO2 gas from CO2/Air mixture with operating parameters.
From Figure 2 – Figure 9, the Absorption rate of CO2 gas from CO2/Air gas mixture (RA) is increased with the
increase in gas mixture flow rate (G), inlet CO2 gas concentration (CCO2), aqueous NaOH solution (CNaOH), and
liquid holdup (VL). The biggest effect of operating parameters on Absorption rate was CCO2 , and smallest one was
VL.
3.2. Correlation Model of Absorption Rate
Computer program (Statgraphics/Experimental Design) was used to estimate the fitted linear model of
absorption rate (RA) for CO2 gas absorption from CO2/air gas mixture into aqueous NaOH solution in packed column
in terms of operating parameters: G, CCO2, CNaOH, and VL. The output shows the results of fitting a multiple linear
regression model to describe the relationship between absorption rate and 4 independent variables.
The equation of the fitted model is:
RA = - 12.877 + 0.020*G + 24.810*CCO2 + 2.87*CNaOH + 193.583*VL (9)
Since the P-value in the ANOVA Table 3 is less than 0.05, there is a statistically significant relationship
between the variables at the 95.0% confidence level.
The R-Squared statistic indicates that the model as fitted explains 91.7659 % of the variability in Absorption
rate. The adjusted R-squared statistic, which is more suitable for comparing models with different numbers of
independent variables, is 89.4133 %. The standard error of the estimate shows the standard deviation of the
residuals to be 1.7619. This value can be used to construct prediction limits for new observations by selecting the
Reports option from the text menu. The mean absolute error (MAE) of 1.17437 is the average value of the residuals.
The Durbin-Watson (DW) statistic tests the residuals to determine if there is any significant correlation based on the
order in which they occur in your data file. Since the P-value is greater than 0.05, there is no indication of serial
autocorrelation in the residuals at the 95.0% confidence level.
In determining whether the model can be simplified, notice that the highest P-value on the independent variables
is 0.2085, belonging to Liquid holdup. Since the P-value is greater or equal to 0.05, that term is not statistically
significant at the 95.0 % or higher confidence level. Consequently, you should consider removing Liquid holdup
from the model.
Table-3. ANOVA
Standard T
Parameter Estimate Error Statistic P-value
Constant -12.8765 4.54644 -2.83221 0.0133
CO2 concentration 24.810 2.20238 11.2651 0.0000
Gas flow rate 0.0200444 0.00489417 4.09557 0.0011
Liquid holdup 193.583 146.825 1.31846 0.2085
NaOH concentration 2.8695 0.880951 3.25727 0.0057
Scientific Review, 2017, 3(5): 43-53
51
The validity range for the model in equation (9) is:
360 ≤ G ≤ 540 m3
/h
0.022 ≤ VL ≤ 0.028 m3
1 ≤ CNaOH≤ 2 M
0. 1 ≤ CCO2 ≤ 0. 5 vol. %
The accuracy of the RA model is 1.7619 %.
The linear model in equation (9) is adequate, and the operating parameters were significant accept VL and were
in ordered of CCO2 G CNaOH VL. The interactions of operating parameters were negligible.
The Pareto Chart of Absorption rate (RA) of CO2 gas from CO2/Air gas mixture could be seen in Figure10:
Figure-10. Pareto chart for Absorption rate of CO2 gas from CO2/Air gas mixture.
The main effects of operating parameters on Absorption rate of CO2 gas from gas mixture CO2/Air is seen
in following Figure 11:
Figure-11. Main effects of operating parameters on Absorption rate of CO2 gas from CO2/Air gas mixture.
The observed and predicted Absorption rate of CO2 gas from CO2/Air gas mixture represents in following
Figure 12:
Scientific Review, 2017, 3(5): 43-53
52
Figure-12. Observed vs. predicted Absorption rate of CO2 gas from CO2/Air gas mixture.
The residual plot for Absorption rate of CO2 gas from CO2/Air gas mixture would be seen in Figure 13:
Figure-13. Residual plot for Absorption rate of CO2 gas from CO2/Air gas mixture.
3.3. Optimal Response
The optimum operating parameters for present work were obtained using the computer program to analyze the
experimental results. The goal of optimizing was to maximize the Absorption rate (RA) of CO2 gas from CO2/Air gas
mixture. The results of optimizing were summarized in Table 4:
Table-4. Optimum operating parameters and optimum Absorption rate of CO2 gas from CO2/Air gas mixture.
Operating parameters Low value High value Optimum value
Gas mixture flow rate (m3
/h):
CO2 gas inlet conc. (vol. %):
NaOH solution conc. (M):
Liquid hold up in column (m3
):
360
0.1
1
0.022
540
0.5
2
0.028
540
0.5
2
0.028
Absorption rate of CO2 gas from CO2/Air gas mixture (k-mol/h): 21.5119
Scientific Review, 2017, 3(5): 43-53
53
4. Conclusions
* Absorption of CO2 gas from CO2/Air gas mixture into NaOH solution was carried out in pilot scale packed
column. The Absorption rate (RA) of CO2 gas was measured at various operating conditions (G, CCO2, CNaOH, and VL)
according to experimental design. The measured Absorption rate was in the range of RA= 3.235 – 22.340 k-mol/h.
The RA could be improved and increases by increasing in the G, CCO2, CNaOH, and VL.
* A computer program (Statgraphics/Experimental Design) was used to estimate the linear fitted model of
Absorption rate (RA) in terms of operating conditions (G, CCO2, CNaOH, and VL. The linear fitted model of RA was
adequate, and operating parameters were significant, while the interactions were negligible. The accuracy of
Absorption rate model is 1.7619 %.
* Using the same computer program the optimum operating conditions were obtained with values of G = 540
m3
/h, CCO2 = 0.5 vol. %., CNaOH = 2 M ,and VL = 0.028 m3
. The optimum Absorption rate (RA) was in value of
21.5119 k-mol/h.
* On the base of results of measured Absorption rate, we conclude to scaling up the size of the pilot plant used
in present work by 3-4 times to commercial size plant and using the optimum operating parameters obtained in
future work.
References
[1] Kim, S. and Kim, H. T., 2004. "Aspen simulation of CO2 absorption system various amine solution."
Prepr. Pap. Am. Chem. Soc. Div. Fuel chem., vol. 49, pp. 251-252.
[2] Yang, H., Xu, Z., Fan, M., Cupta, R., Slimanes, R. B., Bland, A. E., and Wrigth, I., 2008. "Process in
carbon dioxide separation and capture: A review." J. of Environment science, vol. 20, pp. 14-27.
[3] Tee, H. and Yonanes, 2012. "A kinetic and process modeling study of CO2 capture with MEA-Promoted
potassium carbonate solutions." Chem. Eng. Sci., vol. 210, pp. 271-279.
[4] Stewart, C. and Hessami, M., 2005. "A study of methods of carbon dioxide capture and sequestration the
sustainability of a photosynthetic bioreactor approach." Enrg. Conversion and manag, vol. 46, pp. 403-420.
[5] Chen, P. C., Shi, W., Du, R., and Chen, V., 2008. "Scrubbing of CO2 greenhouse gas accompanying with
precipitation in a continuous bubble-column scrubber, I & EC." vol. 49, pp. 6336-6343.
[6] Rochelle, G. T., 2009. "Amine scrubbing for CO2 capture, Science." vol. 325, p. 1652.
[7] Sunho, C., Jeffrey, H. D., and Christopher, W. J., 2009. "Adsorbent materials for carbon dioxide capture
from large anthropogenic point sources." Chem. Sub Chem., vol. 2, pp. 796-854.
[8] Majeed, J. G., 1995. "Comparison of the efficiencies of sulfur dioxide absorption using calcium carbonate
slurry and sodium hydroxide solution in ALT reactor." Gas Sep. Purif, vol. 9, pp. 111-120.
[9] Zeman, F. S. and Lackner, K. S., 2004. "Capturing carbon dioxide directly from the atmosphere." Word
Resour. Rev., vol. 16, pp. 157-172.
[10] Majeed, J. G., 2014. "Absorption of nitrogen dioxide from gas mixture in packed bed column." Inter. J. of
Modern Eng. Res., vol. 4, pp. 23-35.
[11] Bekassy-Molnar, E., Marki, E., and Majeed, J. G., 2005. "Sulfur dioxide absorption in air-lift absorbers by
sodium citrate buffer solution." Chem. Eng. and Processing, vol. 44, pp. 1039-1046.
[12] Majeed, J. G., 2017. "Recovery of sulfur dioxide from gas mixture in packed bed column." Inter. J. of
Energ. Env., vol. 8, pp. 73-82.
[13] Majeed, J. G., 2014. "Volumetric of mass transfer coefficient of SO2 gas absorption into aqueous sodium
sulphite solution in plate column." Modern Applied Science, vol. 8, pp. 59-67.

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Absorption Rate of Carbon Dioxide from Gas Mixture

  • 1. Scientific Review ISSN(e): 2412-2599, ISSN(p): 2413-8835 Vol. 3, No. 5, pp: 43-53, 2017 URL: http://arpgweb.com/?ic=journal&journal=10&info=aims 43 Academic Research Publishing Group Absorption Rate of Carbon Dioxide from Gas Mixture Jafar Ghani Majeed Department of Materials Engineering, College of Engineering, Al-Mustansiriyah University, Baghdad, Iraq 1. Introduction Carbon dioxide is one of the more frequent found gases on the earth. It is a main product in combustion processes and the natural metabolism of living organisms. Carbon dioxide discharged by the consumption of fossil fuel for power and heat production is said to occupy nearly 35- 40 % of the amount of discharged CO2 all over the world [1-3]. Environmental issues caused by exhaust greenhouse gases (GHG) and toxics have become global problems. Through the past studies of five decades, increased GHG levels in atmosphere is believed to cause global warming, in which CO2 is the largest contributors. International Panel on Climate Change (IPCC) predicts that the CO2 content in atmosphere may contain up to 570 ppm CO2, causing an increase in mean global temperature around 1.9℃ and an increase mean sea level of 38 m [4]. Also accompanied is species extinction. Indoor CO2 levels usually vary between 400 and 2000 ppm (parts per million). Outdoor CO2 levels are usually 350 - 450 ppm. Heavily industrialized or contaminated areas may periodically have a CO2 concentration of up to 800 ppm. The levels of outdoor CO2 are higher in areas where traffic is very heavy. CO2 must not be confused with carbon monoxide (CO), a very toxic gas that is a by-product from poor combustion in i.e. cars and fireplaces. Carbon monoxide is dangerous at very low concentrations (25 to 50 ppm). In industrial environments where process generated CO2 dominates (or CO2 not generated by people), for example in breweries, packaging industry, freezer storages etc, the maximum Permitted CO2 concentration according to most standards is as high as 5000 ppm during an 8-hour working period. You will not find such high levels in a home or in an office environment where people are the main source of carbon dioxide. Several methods have been proposed to remove CO2 from the air, or from flue gases, such as chemical absorption, physical absorption, membrane separation, biochemical methods, and the catalytic conversion method. In addition to these methods, the absorption of carbon dioxide in an alkaline solution with crystallization has also been adopted to explore the removal of carbon dioxide from waste gas [5]. These usually involve using a variant of the Kraft process. Scrubbing processes may be based on sodium hydroxide [6-8]. The CO2 is absorbed into solution, transferred to lime via a process called causticization and released in a kiln. Some researchers outlined a specific methods of air capture [9-13]. CO2 is absorbed by an alkaline NaOH solution to produce dissolved sodium carbonate. The absorption reaction is a gas liquid reaction, strongly exothermic, (below): 2NaOH (aq) + CO2 (g) → Na2CO3 (aq) + H2O (1) The mechanism of reaction between the acidic oxide and the alkali depends on the concentration of the alkali solution. Abstract: Absorption of CO2 gas from CO2/Air mixture into aqueous sodium hydroxide solution has been achieved using packed column in pilot scale at constant temperature (T) of 25±1℃.The aim of the present work was to improve the Absorption rate of this process, to find the optimal operation conditions, and to contribute to the using of this process in the chemical industry. Absorption rate (RA) was measured by using different operating parameters: gas mixture flow rate (G) of 360-540 m3/h, carbon dioxide inlet concentration (CCO2) of 0.1-0.5 vol. %, NaOH solution concentration (CNaOH) of 1-2 M, and liquid holdup in the column (VL) of 0.022- 0.028 m3 according to experimental design. The measured RA was in the range of RA = 3.235 – 22.340 k-mol/h. Computer program (Statgraphics/Experimental Design) was used to estimate the fitted linear model of RA in terms of (G, CCO2, CNaOH, and VL), and the economic aspects of the process. R-squared of RA model was 91.7659 percent, while the standard error of the estimate shows the standard deviation of the residuals to be 1.7619. The linear model of RA was adequate, the operating parameters were significant except the liquid holdup was not significant, and the interactions were negligible. Keywords: Packed column; CO2 absorption; NaOH solution; Absorption rate.
  • 2. Scientific Review, 2017, 3(5): 43-53 44 (a) When the alkali (NaOH) solution is very dilute (pH < 8), carbon dioxide first reacts with water to form carbonic acid (H2CO3) slowly. The acid thus formed then reacts with the alkali to give sodium hydrogen carbonate (NaHCO3): CO2 (g) + H2O (l) ↔ H2CO3 (aq) (2) NaOH (aq) + H2CO3 (aq) → NaHCO3 (aq) + H2O (l) (3) (b) When the alkali solution is a fairly concentrated one (pH > 10), carbon dioxide directly reacts with it to form the bicarbonate, which further reacts with the alkali to form sodium carbonate (Na2CO3) as the main product by complete neutralization: NaOH (aq) + CO2 (g) → NaHCO3 (aq) (4) NaHCO3 (aq) + NaOH (aq) → Na2CO3 (aq) + H2O (l) (5) Thus, only when the concentration of the alkali solution is quite low, the reaction proceeds via the formation of carbonic acid. But the acidic oxide is not completely neutralized in this case. 2. Experimental Work 2.1. Experimental Apparatuses The main equipment of the experimental apparatus as shown in Figure 1 is the packed column (1), with the size of 2 m height and 0.2 m diameter. The main complementary apparatus and pipe lines are as follows: Compressed air (2), carbon dioxide gas (3), flow meter for compressed air (4), flow meter for CO2 gas (5) , mixing gas chamber (6), gas mixture vent (7), thermostat (8), gas mixture into packed column (9), temperature indicator (10), pH indicator (11), gas mixture to CO2 analyzer (12), CO2 analyzer (13), gas vent (14), gas mixture out (15), flow meter for aqueous NaOH solution (16), head tank (17), outlet gas mixture to CO2 gas analyzer (18), aqueous sodium hydroxide solution into packed column (19), product tank (20), aqueous sodium hydroxide solution feed tank (21), feed pump (22), thermostat (23). Figure-1. Schematic diagram of the experimental apparatus for CO2 gas absorption from CO2/Air gas mixture into aqueous NaOH solution in packed column. 20 19 23 22 21 M 17 16 15 18 14 12 13 7 2 3 6 4 5 8 10 11 9 1
  • 3. Scientific Review, 2017, 3(5): 43-53 45 2.2. Operating Parameters The preliminary experiments were carried out to absorb of CO2 gas from gas mixture into aqueous NaOH solution in pilot scale packed column using experimental apparatus as shown in Figure 1 to find the proper operating parameters would be used in this work. Operating variable parameters were as follows: * Gas mixture flow rate (G): 360-540 m3 /h. * CO2 gas inlet concentration (CCO2): 0.1-0.5 vol. %. * Aqueous NaOH solution concentration (CNaOH): 1-2 M. * Liquid temperature (T): 25±1℃. * Liquid holdup in the column (VL): 0.022-0.028 m3 . 2.3. Absorption of CO2 from CO2/Air Gas Mixture Experiments of absorption of CO2 gas from CO2/Air gas mixture into aqueous NaOH solution have been carried out using the mentioned various operating parameters by using experimental apparatus as shown in Figure 1, according to experimental design plan seen in Table 1. The flow rates of compressed air (2) and CO2 gas (3) from gas cylinder were measured by flow meters (4) and (5) respectively, and enter the mixing chamber (6). The gas mixture (9) enters the packed column (1) through the thermostat (8) from lower part. The gas mixture via the gas line (12) enters CO2 gas analyzer (13) to measure CO2 inlet concentration in the gas mixture. Aqueous NaOH solution from NaOH solution feed tank (21) by feed pump (22) enters the upper part of the column through the liquid feeding line (19). The thermostat (23) is maintained the desired liquid temperature constant in packed column (1) during the all experiments runs. One part of gas mixture from the top of column through the gas mixture line (18) was taken into CO2 gas analyzer (13) to measure outlet CO2 gas concentration, while the other part of gas mixture discharge to atmosphere via the gas mixture line (15). In the column, the liquid temperature measured by temperature gage (10), while the pH of the liquid is measured by digital pH-meter (11). The resultant reaction product Na2CO3 solution from downer part of column sent to solution product tank (20). Table-1. Experimental design plan for absorption of CO2 into aqueous NaOH solution. Liquid holdup in the column (VL) NaOH solution concentration (CNaOH) CO2 gas inlet concentration (CCO2) Gas mixture flow rate (G) Run No. (m3 )(M)(vol. %)(m3 /h) 0.0251.50.34501 0.02220.55402 0.02810.53603 0.02210.13604 0.02220.53605 0.02820.55406 0.02810.13607 0.0251.50.34508 0.02820.13609 0.0251.50.345010 0.02220.136011 0.02810.154012 0.02820.536013 0.02210.536014 0.02220.154015 0.02210.554016 0.02210.154017 0.02820.154018 0.02810.554019 2.4. Definition of CO2 Absorption Rate The CO2 inlet flow rate (Gin) is calculated using the following equation: Gin = [(Qair x Dair /Mair)/ (1 –YCO2, in)] YCO2, in (6) Where, Gin = CO2 inlet flow rate, k-mol/h.
  • 4. Scientific Review, 2017, 3(5): 43-53 46 Qair =Air volumetric flow rate, m3 /h. Dair = Density of air, kg/m3 at standard conditions. Mair = Molecular weight of air, kg/k-mol. YCO2, in = CO2 mole fraction at inlet of packed column, vol. %. The CO2 outlet flow rate (Gout) is calculated using the following equation: Gout = [(Qair xDair/Mair)/ (1-YCO2, out)]YCO2, out (7) Where, Gout = CO2 outlet flow rate, k-mol/h. YCO2, out = CO2 mole fraction at outlet of packed column, vol. %. The CO2 absorption rate (RA) is the difference between the inlet and outlet CO2 flow rates [14 -17]: RA = Gin – Gout (8) Where, RA = CO2 absorption rate, k-mol/h. 3. Results and Discussion 3.1. Absorption Rate Calculation The absorption of CO2 gas from CO2/Air gas mixture into aqueous sodium hydroxide (NaOH) solution were carried out according to experimental design plan in Table 1 with the variation of gas mixture flow rate (G), CO2 gas inlet concentration (CCO2), , aqueous NaOH solution concentration (CNaOH), and liquid holdup in the column (VL). Absorption rate (RA) was calculated by using equation (4). The RA of CO2 gas from gas mixture CO2/Air was in the range of RA = 3.235 – 22.340 k-mol/h. The results of RA are summarized in Table 2: Table-2. Data base of experimental design and results of CO2 gas absorption from gas mixture CO2 /Air into aqueous NaOH solution. Absorptio n rate (RA) Liquid holdup in the column (VL) NaOH solution concentration (CNaOH) CO2 gas inlet concentration (CCO2) Gas mixture flow rate (G) Run No. (k-mol/h)(m3 )(M)(vol. %)(m3 /h) 12.3500.0251.50.34501 21.2040.02220.55402 14.2600.02810.53603 3.2350.02210.13604 16.6160.02220.53605 22.3400.02820.55406 7.5430.02810.13607 13.5640.0251.50.34508 10.4540.02820.13609 11.8950.0251.50.345010 7.4300.02220.136011 5.5500.02810.154012 14.6500.02820.536013 13.4140.02210.536014 9.4500.02220.154015 18.7310.02210.554016 7.3080.02210.154017 11.3680.02820.154018 20.5150.02810.554019
  • 5. Scientific Review, 2017, 3(5): 43-53 47 The effects of operating parameters on absorption rate of CO2 gas from CO2/Air gas mixture could be seen as in the following Figures: Figure-2. Effect of CO2 gas inlet concentration, and gas mixture flow rate on Absorption rate of CO2 gas from CO2/Air mixture. Figure-3. Effect of NaOH concentration, and gas mixture flow rate on Absorption rate of CO2 gas from CO2/Air mixture.
  • 6. Scientific Review, 2017, 3(5): 43-53 48 Figure-4. Effect of liquid holdup,, and gas mixture flow rate on Absorption rate of CO2 gas from CO2/Air mixture. Figure-5. Effect of aqueous NaOH concentration, and CO2 inlet concentration on Absorption rate of CO2 gas from CO2/Air mixture. Figure-6. Effect of aqueous NaOH concentration, and liquid holdup on Absorption rate of CO2 gas from CO2/Air mixture.
  • 7. Scientific Review, 2017, 3(5): 43-53 49 Figure-7. Effect of CO2 inlet concentration, and liquid holdup on Absorption rate of CO2 gas from CO2/Air mixture. The 3 D sequential Graphs/Box plot and Block plot for Absorption rate (RA) with independent parameters: gas mixture flow rate (G), inlet CO2 gas concentration (CCO2), aqueous NaOH solution (CNaOH), and liquid holdup (VL) as in the following figures: Figure-8. 3 D sequential Graph/Box plot for Absorption rate of CO2 gas from CO2/Air mixture with operating parameters.
  • 8. Scientific Review, 2017, 3(5): 43-53 50 Figure-9. 3 D sequential Graph/Block plot for Absorption rate of CO2 gas from CO2/Air mixture with operating parameters. From Figure 2 – Figure 9, the Absorption rate of CO2 gas from CO2/Air gas mixture (RA) is increased with the increase in gas mixture flow rate (G), inlet CO2 gas concentration (CCO2), aqueous NaOH solution (CNaOH), and liquid holdup (VL). The biggest effect of operating parameters on Absorption rate was CCO2 , and smallest one was VL. 3.2. Correlation Model of Absorption Rate Computer program (Statgraphics/Experimental Design) was used to estimate the fitted linear model of absorption rate (RA) for CO2 gas absorption from CO2/air gas mixture into aqueous NaOH solution in packed column in terms of operating parameters: G, CCO2, CNaOH, and VL. The output shows the results of fitting a multiple linear regression model to describe the relationship between absorption rate and 4 independent variables. The equation of the fitted model is: RA = - 12.877 + 0.020*G + 24.810*CCO2 + 2.87*CNaOH + 193.583*VL (9) Since the P-value in the ANOVA Table 3 is less than 0.05, there is a statistically significant relationship between the variables at the 95.0% confidence level. The R-Squared statistic indicates that the model as fitted explains 91.7659 % of the variability in Absorption rate. The adjusted R-squared statistic, which is more suitable for comparing models with different numbers of independent variables, is 89.4133 %. The standard error of the estimate shows the standard deviation of the residuals to be 1.7619. This value can be used to construct prediction limits for new observations by selecting the Reports option from the text menu. The mean absolute error (MAE) of 1.17437 is the average value of the residuals. The Durbin-Watson (DW) statistic tests the residuals to determine if there is any significant correlation based on the order in which they occur in your data file. Since the P-value is greater than 0.05, there is no indication of serial autocorrelation in the residuals at the 95.0% confidence level. In determining whether the model can be simplified, notice that the highest P-value on the independent variables is 0.2085, belonging to Liquid holdup. Since the P-value is greater or equal to 0.05, that term is not statistically significant at the 95.0 % or higher confidence level. Consequently, you should consider removing Liquid holdup from the model. Table-3. ANOVA Standard T Parameter Estimate Error Statistic P-value Constant -12.8765 4.54644 -2.83221 0.0133 CO2 concentration 24.810 2.20238 11.2651 0.0000 Gas flow rate 0.0200444 0.00489417 4.09557 0.0011 Liquid holdup 193.583 146.825 1.31846 0.2085 NaOH concentration 2.8695 0.880951 3.25727 0.0057
  • 9. Scientific Review, 2017, 3(5): 43-53 51 The validity range for the model in equation (9) is: 360 ≤ G ≤ 540 m3 /h 0.022 ≤ VL ≤ 0.028 m3 1 ≤ CNaOH≤ 2 M 0. 1 ≤ CCO2 ≤ 0. 5 vol. % The accuracy of the RA model is 1.7619 %. The linear model in equation (9) is adequate, and the operating parameters were significant accept VL and were in ordered of CCO2 G CNaOH VL. The interactions of operating parameters were negligible. The Pareto Chart of Absorption rate (RA) of CO2 gas from CO2/Air gas mixture could be seen in Figure10: Figure-10. Pareto chart for Absorption rate of CO2 gas from CO2/Air gas mixture. The main effects of operating parameters on Absorption rate of CO2 gas from gas mixture CO2/Air is seen in following Figure 11: Figure-11. Main effects of operating parameters on Absorption rate of CO2 gas from CO2/Air gas mixture. The observed and predicted Absorption rate of CO2 gas from CO2/Air gas mixture represents in following Figure 12:
  • 10. Scientific Review, 2017, 3(5): 43-53 52 Figure-12. Observed vs. predicted Absorption rate of CO2 gas from CO2/Air gas mixture. The residual plot for Absorption rate of CO2 gas from CO2/Air gas mixture would be seen in Figure 13: Figure-13. Residual plot for Absorption rate of CO2 gas from CO2/Air gas mixture. 3.3. Optimal Response The optimum operating parameters for present work were obtained using the computer program to analyze the experimental results. The goal of optimizing was to maximize the Absorption rate (RA) of CO2 gas from CO2/Air gas mixture. The results of optimizing were summarized in Table 4: Table-4. Optimum operating parameters and optimum Absorption rate of CO2 gas from CO2/Air gas mixture. Operating parameters Low value High value Optimum value Gas mixture flow rate (m3 /h): CO2 gas inlet conc. (vol. %): NaOH solution conc. (M): Liquid hold up in column (m3 ): 360 0.1 1 0.022 540 0.5 2 0.028 540 0.5 2 0.028 Absorption rate of CO2 gas from CO2/Air gas mixture (k-mol/h): 21.5119
  • 11. Scientific Review, 2017, 3(5): 43-53 53 4. Conclusions * Absorption of CO2 gas from CO2/Air gas mixture into NaOH solution was carried out in pilot scale packed column. The Absorption rate (RA) of CO2 gas was measured at various operating conditions (G, CCO2, CNaOH, and VL) according to experimental design. The measured Absorption rate was in the range of RA= 3.235 – 22.340 k-mol/h. The RA could be improved and increases by increasing in the G, CCO2, CNaOH, and VL. * A computer program (Statgraphics/Experimental Design) was used to estimate the linear fitted model of Absorption rate (RA) in terms of operating conditions (G, CCO2, CNaOH, and VL. The linear fitted model of RA was adequate, and operating parameters were significant, while the interactions were negligible. The accuracy of Absorption rate model is 1.7619 %. * Using the same computer program the optimum operating conditions were obtained with values of G = 540 m3 /h, CCO2 = 0.5 vol. %., CNaOH = 2 M ,and VL = 0.028 m3 . The optimum Absorption rate (RA) was in value of 21.5119 k-mol/h. * On the base of results of measured Absorption rate, we conclude to scaling up the size of the pilot plant used in present work by 3-4 times to commercial size plant and using the optimum operating parameters obtained in future work. References [1] Kim, S. and Kim, H. T., 2004. "Aspen simulation of CO2 absorption system various amine solution." Prepr. Pap. Am. Chem. Soc. Div. Fuel chem., vol. 49, pp. 251-252. [2] Yang, H., Xu, Z., Fan, M., Cupta, R., Slimanes, R. B., Bland, A. E., and Wrigth, I., 2008. "Process in carbon dioxide separation and capture: A review." J. of Environment science, vol. 20, pp. 14-27. [3] Tee, H. and Yonanes, 2012. "A kinetic and process modeling study of CO2 capture with MEA-Promoted potassium carbonate solutions." Chem. Eng. Sci., vol. 210, pp. 271-279. [4] Stewart, C. and Hessami, M., 2005. "A study of methods of carbon dioxide capture and sequestration the sustainability of a photosynthetic bioreactor approach." Enrg. Conversion and manag, vol. 46, pp. 403-420. [5] Chen, P. C., Shi, W., Du, R., and Chen, V., 2008. "Scrubbing of CO2 greenhouse gas accompanying with precipitation in a continuous bubble-column scrubber, I & EC." vol. 49, pp. 6336-6343. [6] Rochelle, G. T., 2009. "Amine scrubbing for CO2 capture, Science." vol. 325, p. 1652. [7] Sunho, C., Jeffrey, H. D., and Christopher, W. J., 2009. "Adsorbent materials for carbon dioxide capture from large anthropogenic point sources." Chem. Sub Chem., vol. 2, pp. 796-854. [8] Majeed, J. G., 1995. "Comparison of the efficiencies of sulfur dioxide absorption using calcium carbonate slurry and sodium hydroxide solution in ALT reactor." Gas Sep. Purif, vol. 9, pp. 111-120. [9] Zeman, F. S. and Lackner, K. S., 2004. "Capturing carbon dioxide directly from the atmosphere." Word Resour. Rev., vol. 16, pp. 157-172. [10] Majeed, J. G., 2014. "Absorption of nitrogen dioxide from gas mixture in packed bed column." Inter. J. of Modern Eng. Res., vol. 4, pp. 23-35. [11] Bekassy-Molnar, E., Marki, E., and Majeed, J. G., 2005. "Sulfur dioxide absorption in air-lift absorbers by sodium citrate buffer solution." Chem. Eng. and Processing, vol. 44, pp. 1039-1046. [12] Majeed, J. G., 2017. "Recovery of sulfur dioxide from gas mixture in packed bed column." Inter. J. of Energ. Env., vol. 8, pp. 73-82. [13] Majeed, J. G., 2014. "Volumetric of mass transfer coefficient of SO2 gas absorption into aqueous sodium sulphite solution in plate column." Modern Applied Science, vol. 8, pp. 59-67.