Mechanism of gas absorption with two-phase absorbents
Introduction
The gas absorption of components in gas mixtures with high (HCl), middle (SO2) and low (CO2) solubility in the water, by means of two-phase absorbents, where the active components (CaCO3, Ca(OH)2) are water suspensions, is used in power plants for gas cleaning (absorption of SO2 in waste gases) or solutions of lime neutralization by CO2 absorption (in calcinated soda production plants). In the first case SO2 is possible to be examined also as a high soluble gas.
The presence of the active component in the absorbent as solution and solid phase leads to an increasing of the absorption capacity of the absorbent, but the introduction of a new process (the solution of the solid phase) creates conditions for variation of the absorption mechanism (interphase mass transfer through two interphase surfaces – gas/liquid and liquid/solid).
Section snippets
Physical model
As a physical model will be used a laminar co-current gas–liquid flow in vertical canal with flat walls (Fig. 1), where the liquid flowing down as a liquid film.
The gas flow is a mixture and an active component dissolves in the liquid film, where reacts with the active component of the absorbent, dissolved in the liquid. The solid walls are made from the same active component of the absorbent and dissolve in the liquid film. The chemical reaction between active components (reagents) of the gas
Hydrodynamic model
Let us consider co-current flow of a laminar gas flow and laminar liquid film flow and and are the average velocities (m s−1):where QG and QL (m3 m−1 s−1) are the gas and liquid flow rates in a canal with a width of one meter.
The velocity distributions in the gas and liquid phases will be obtained in the stratified flows approximations [1], [2]:
The large difference between values of gas and liquid viscosity coefficients permit the friction force between
Interphase mass transfer model
The obtained solutions (6) of the hydrodynamic problem permit to be used the convection–diffusion equations for the formulation of the interphase mass transfer model in thin layer approximation In (7), (8), (9) (m2 s−1) are the diffusivities of the reagents in
Absorption kinetics
The presented theoretical analysis of the gas absorption with two-phase absorbents shows, that the absorption rate depends on the rates of four processes:
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mass transfer from the gas volume to the gas–liquid interphase surface;
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mass transfer from the gas–liquid interphase surface to the liquid volume;
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mass transfer from the solid–liquid interphase surface to the liquid volume;
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chemical reaction in the liquid volume.
In the general case the absorption rate is possible to be obtained after solution of
Absorption mechanism
The identification of the absorption mechanism needs a mass balance of the reagents in the film flow volume Δv = hΔx (m3) with width of 1 (m), thickness of h (m) and length of Δx (m).
The diffusion mass flux of the active gas component JD (kg mol m−1 s−1), which enters in the volume Δv across the gas–liquid interphase surface Δs1 = Δx (m2) (with width of 1 (m)) is:
The convective mass flux of the active gas component JC (kg mol m−1 s−1), which enters in the volume Δv across the liquid
Absorption of gases with high solubility
The relations (24), (25), (26) permit to be obtained the influence of the mass fluxes at the phase boundaries on the process mechanism.
In the cases of gases with high solubility (SO2, HCl) and (for example ) and the problem (12) is possible to be solved in approximation . As a result and the model (11), (12), (13) must be reduced:
Absorption of gases with low solubility
In the cases of gases with low solubility (CO2) and (for example ) and the problem (11) is possible to be solved in approximation . As a result the problem (11) must be replaced by and the last boundary condition in (12) by Y = 1, C1 = 1:
The solution of (32), (33) permits to be obtained and kL, using (16).
From (32) follows, that for
Conclusions
The two-phase absorbent (water suspensions of CaCO3 or Ca(OH)2) are used in power plants for waste gases cleaning (absorption of SO2). This process is used in calcinated soda plants for solutions of lime neutralization by CO2.
The presented theoretical analysis shows, that the using of two-phase absorbents leads to modification of the absorption mechanism as a result of the new mass transfer resistance at the liquid–solid interphase surface. The absorption mechanisms for the practically
References (4)
- et al.
Mass Transfer in Liquid Film Flows
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Mass Transfer in Following Liquid Films
(1984)
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