+ All Categories
Home > Documents > INFLUENCE OF VERTICAL DISTRIBUTION OF ABSORBATE IN A GASEOUS PHASE ON GAS ABSORPTION BY FALLING...

INFLUENCE OF VERTICAL DISTRIBUTION OF ABSORBATE IN A GASEOUS PHASE ON GAS ABSORPTION BY FALLING...

Date post: 16-Dec-2015
Category:
Upload: luz-molin
View: 214 times
Download: 1 times
Share this document with a friend
Popular Tags:
17
INFLUENCE OF VERTICAL DISTRIBUTION OF ABSORBATE IN A GASEOUS PHASE ON GAS ABSORPTION BY FALLING LIQUID DROPLET T. Elperin, A. Fominykh and B. Krasovitov Department of Mechanical Engineering The Pearlstone Center for Aeronautical Engineering Studies Ben-Gurion University of the Negev P.O.B. 653, Beer Sheva 84105, ISRAEL
Transcript

INFLUENCE OF VERTICAL DISTRIBUTION OF ABSORBATE IN A GASEOUS PHASE ON GAS ABSORPTION BY FALLING LIQUID DROPLET

T. Elperin, A. Fominykh and B. Krasovitov

Department of Mechanical EngineeringThe Pearlstone Center for Aeronautical

Engineering Studies Ben-Gurion University of the Negev

P.O.B. 653, Beer Sheva 84105, ISRAEL

Motivation and goals

Fundamentals

Description of the model

Results and discussion

Conclusions

Outline of the presentation

Ben-Gurion University of the NegevILASS Europe, Como 2008

Gas absorption by falling droplets

Ben-Gurion University of the Negev

Single Droplet

• SO2 absorption of boiler flue gas

• HF absorption in the aluminum industry

• In-cloud scavenging of polluted gases (SO2, CO2, CO, NOx, NH3)

Air

Soluble gas

Scavenging of air pollutions by cloud and rain droplets

is the species indissolved state

Henry’s Law:

Spray towerabsorbers

Sprayscrubbers

Vertical concentration gradient of soluble gases

Ben-Gurion University of the Negev

Scavenging of air pollutionsAbsorbers

– different rates of gas absorption by droplets at the inlet and outlet of the

absober

Gaseous pollutions in atmosphere– SO2 and NH3 – anthropogenic emission

– CO2 – competition between photosynthesis, respiration and

thermally driven buoyant mixing

Fig. 1. Aircraft observation of vertical profiles of CO2 concentration (by Perez-Landa et al., 2007)

ILASS Europe, Como 2008

Gas absorption by falling droplets:

• Walcek and Pruppacher, 1984• Alexandrova et al., 2004• Elperin and Fominykh, 2005

Measurements of vertical distribution of trace gases in the atmosphere:

• SO2 – Gravenhorst et al., 1978• NH3 – Georgii and Müller, 1974• CO2 – Denning et al., 1995; Perez-Landa et al., 2007

Effect of vertical distribution of absorbate in a gaseous phase on gas absorption by falling droplet:

• Elperin, Fominykh and Krasovitov 2008

Gas absorption by falling droplets:

• Walcek and Pruppacher, 1984• Alexandrova et al., 2004• Elperin and Fominykh, 2005

Measurements of vertical distribution of trace gases in the atmosphere:

• SO2 – Gravenhorst et al., 1978• NH3 – Georgii and Müller, 1974• CO2 – Denning et al., 1995; Perez-Landa et al., 2007

Effect of vertical distribution of absorbate in a gaseous phase on gas absorption by falling droplet:

• Elperin, Fominykh and Krasovitov 2008

Scientific background

Ben-Gurion University of the NegevILASS Europe, Como 2008

Description of the model

Ben-Gurion University of the Negev

In the analysis we used the following assumptions:

c << R

Tangential molecular mass transfer rate along the surface is small compared with a molecular mass transfer rate in the normal

direction

The bulk of a droplet, beyond the diffusion boundary layer, is completely mixed by

circulations inside a droplet and concentration of absorbate is homogeneous

in the bulkThe droplet has a spherical shape.

Fig. 1. Schematic view of a falling droplet and concentration profile

0.1 mm R 0.5 mm

10 Re 300

0.7 U 4.5 m/s

ILASS Europe, Como 2008

Description of the model

Ben-Gurion University of the Negev

sinkUv cos2

yR

kUr v

2

2cos2sin

Y

X

Y

XY

XPe

X iiii

i

i

Fluid velocity components at the gas-liquid interface are (Prippacher & Klett, 1997):

(1)

Transient equations of convective diffusion for the liquid and gaseous phases read:

(2)(i = 1, 2)

.Ry where k = 0.009 0.044 for different Re, and

where

,2010

2011

bb

b

mxx

mxxX

,2010

2022

bb

b

mxx

xxX

ii D

RkUPe ,

2R

tDii ,

R

yY

xi– molar fraction of i-th species;

xb10– initial molar fraction of absorbate in

a droplet;

xb20– molar fraction of absorbate in a gas

phase at height H ;

m– dimensionless Henry constant

ILASS Europe, Como 2008

Description of the model

Ben-Gurion University of the Negev

Boundary conditions:

wherey

xCDN i

iii

)( 222 bXX at Y

)( 111 bXX at Y

21 XmX at 0Y

21 NN at 0Y

(3)

(4)

(5)

(6)

ILASS Europe, Como 2008

Method of the solution

Ben-Gurion University of the NegevILASS Europe, Como 2008

Method of the solution

Ben-Gurion University of the Negev

Integral material balance over the droplet yields:

dNRtd

xdVC Y

b sin20

0121

1 (8)

Expression for absorbate concentration in the bulk of a droplet is the following :

0 10

211

1 ),(

sin)()(

)1(

31)( d

TXmX

DmPeTX

T

bbb (9a)

For the linear vertical distribution of absorbate in the gaseous phase:

0 10

11

1 ),(

sin)(

)1(

31)( d

T

dBX

DmPeTX

T

bb (9b)

ground on the absorbatean ofion concentrat is,)(

)(200

2010

20200b

bx

Hkmxx

RxxmB

ILASS Europe, Como 2008

where

Method of the solution

Ben-Gurion University of the NegevILASS Europe, Como 2008

The method of solution is based on the approximate calculation of a definite integral using some quadrature formula:

The uniform mesh with an increment h was used:

Using trapezoidal integration rule we obtain a system of linear algebraic equations:

Method of numerical solution

Ben-Gurion University of the Negev

],[1

FRFdF Ni

N

ii

b

a

,,bai ,,...,2,1 Ni

where FRN – remainder of the series after the N-th term.

,0 ihTTi N

TTh N 0

NigfKfKhfKh

gf

i

i

jjjiiiii ,,1,)

2

1()

2

11(

),0()0(1

100

ILASS Europe, Como 2008

Results and discussion

Ben-Gurion University of the Negev

Fig. 2. Dependence of the concentration of CO2 in the bulk of a water droplet vs. time (average

concentration of CO2 in the atmosphere is 300 ppm), xb10 = 0.

Fig. 3. Dependence of the concentrattion of CO2 in the bulk of a water droplet vs. time (average

concentration of CO2 in spray absorber is 600 ppm).

ILASS Europe, Como 2008

Results and discussion

Ben-Gurion University of the Negev

Fig. 5. Dependence of the concentration of CO2 in the bulk of a water droplet vs. time

(average concentration of CO2 in the

atmosphere is 300 ppm), xb10 = mxb20.

ILASS Europe, Como 2008

Fig. 4. Dependence of the concentration of the dissolved gas in the bulk of a water

droplet vs. time for absorption of SO2 by

water in the atmosphere, xb10 = 0.

Results and discussion

Ben-Gurion University of the Negev

Fig. 6. Aircraft observation of vertical profiles of CO2 concentration

(by Perez-Landa et al., 2007)

Fig. 7a. Dependence of concentration in the atmosphere on the altitude in the morning

Fig. 7b. Dependence of concentration in the atmosphere on the altitude in the afternoon.

Fig. 8. Dependence of the concentration of the dissolved gas in the bulk of a water droplet vs. time for absorption of CO2 by

water in the atmosphere, xb10 = 0.

Results and discussion

Ben-Gurion University of the Negev

Fig. 9. Dependence of the relative concentration of the dissolved gas at a

ground vs. gradxb2 for absorption of SO2 by water droplet, xb10 = 0, xb20 =

0.01 ppm.

ILASS Europe, Como 2008

Conclusion

Ben-Gurion University of the Negev

Vertical inhomogenity of the soluble gas concentration in the gaseous phase strongly affects mass transfer during gas absorption by falling droplet.

– When concentration of the soluble gases decreases with altitude, droplets absorb trace gases during all their fall.

– When concentration of the soluble trace gases increases with altitude, beginning from some altitude gas absorption is replaced by gas desorption.

Concentration of the dissolved gas in a droplet at the ground is independent of the initial concentration of the dissolved gas in a droplet.

It is showed that when concentration of a soluble gas in a gaseous phase has a maximum on the ground, concentration of the dissolved gas in a droplet on the ground is lower than concentration of saturation in a liquid corresponding to the concentration of trace gas on the ground. On the contrary when concentration of the soluble gas in a gaseous phase has a minimum on the ground, concentration of the dissolved gas in a droplet on the ground is higher than concentration of saturation in a liquid corresponding to concentration of soluble gas on the ground.

ILASS Europe, Como 2008


Recommended