t. elperin, a. fominykh and b. krasovitov department of mechanical engineering

15
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 A. Vikhansky School of Engineering and Material Science Queen Mary University of London, London, UK

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Effect of Rain Scavenging on Altitudinal Distribution of Soluble Gaseous Pollutants in the Atmosphere. T. Elperin, A. Fominykh and B. Krasovitov Department of Mechanical Engineering The Pearlstone Center for Aeronautical Engineering Studies - PowerPoint PPT Presentation

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Page 1: T. Elperin, A. Fominykh and B. Krasovitov Department of Mechanical Engineering

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 84105ISRAEL

A. Vikhansky

School of Engineering and Material ScienceQueen Mary University of London, London, UK

Page 2: T. Elperin, A. Fominykh and B. Krasovitov Department of Mechanical Engineering

Motivation and goals

Fundamentals

Description of the model

Results and discussion

Conclusions

Ben-Gurion University of the NegevQueen Mary University of London

IAAR Conference, JerusalemFebruary 10, 2010

Page 3: T. Elperin, A. Fominykh and B. Krasovitov Department of Mechanical Engineering

Rain Droplet

Atmospheric 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:

• In-cloud scavenging of polluted gases

• Scavenging of air pollutions by rain

Ben-Gurion University of the NegevQueen Mary University of London

IAAR Conference, JerusalemFebruary 10, 2010

Page 4: T. Elperin, A. Fominykh and B. Krasovitov Department of Mechanical Engineering

Scavenging of air pollutionsGaseous pollutants in atmosphere

SO2 and NH3 – anthropogenic emission CO2 – competition between photosynthesis, respiration and thermally driven buoyant

mixing

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

Ben-Gurion University of the NegevQueen Mary University London

IAAR Conference, JerusalemFebruary 10, 2010

Page 5: T. Elperin, A. Fominykh and B. Krasovitov Department of Mechanical Engineering

Fig. 1b. Vertical distribution of SO2. Solid lines - results of calculations with (1) and without (2) wet chemical reaction (Gravenhorst et al. 1978); experimental values (dashed lines) – (a) Georgii & Jost (1964); (b) Jost (1974); (c) Gravenhorst (1975); Georgii (1970); Gravenhorst (1975); (f) Jaeschke et al., (1976)

Scavenging of air pollutionsGaseous pollutants in atmosphere

SO2 and NH3 – anthropogenic emission CO2 – competition between photosynthesis, respiration and thermally driven buoyant

mixing

Ben-Gurion University of the NegevQueen Mary University of London

IAAR Conference, JerusalemFebruary 10, 2010

Page 6: T. Elperin, A. Fominykh and B. Krasovitov Department of Mechanical Engineering

Gas absorption by rain:• Asman, 1995 – uniformly distributed soluble pollutant gas • Slinn, 1974 – wash out of plums• Zhang, 2006 – wash out of soluble pollutants by drizzle

Measurements of vertical distribution of trace gases in the atmosphere:

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

Precipitation scavenging of gaseous pollutants by rain in inhomogeneous atmosphere:

• Elperin, Fominykh & Krasovitov 2009 – non-uniform temperature and concentration distribution in the atmosphere (single droplet)

• Elperin et al. 2010 – Effect of Rain Scavenging on Altitudinal Distribution of Soluble Gaseous Pollutants in the Atmosphere

Ben-Gurion University of the NegevQueen Mary University of London

IAAR Conference, JerusalemFebruary 10, 2010

Page 7: T. Elperin, A. Fominykh and B. Krasovitov Department of Mechanical Engineering

Integral mass balance of the dissolved gas in a droplet:

characteristic diffusion time

3ma

D

LG

D

Lcmc

dtdc

1

where

m solubility parameter

mass transfer coefficient in a gaseous phase Gc concentration of a soluble gaseous pollutant in a gaseous phase

mixed-average concentration of the dissolved gas in a droplet Lc

(1)

Ben-Gurion University of the NegevQueen Mary University London

IAAR Conference, JerusalemFebruary 10, 2010

Page 8: T. Elperin, A. Fominykh and B. Krasovitov Department of Mechanical Engineering

For small Eq. (1) yields:

(1)

Dimensionless mass transfer coefficient for a falling droplet in a case of gaseous phase controlled mass transfer:

(2)

dDGSh

3121 ScRe6.02Sh

Ben-Gurion University of the NegevQueen Mary University of London

IAAR Conference, JerusalemFebruary 10, 2010

D

tdcdcmcG

DGL (3)

Total concentration of soluble gaseous pollutant in gaseous and liquid phases reads:

(4) LG ccc 1

Page 9: T. Elperin, A. Fominykh and B. Krasovitov Department of Mechanical Engineering

Since

(5)

(6)

Ben-Gurion University of the NegevQueen Mary University of LondonIAAR Conference, Jerusalem

February 10, 2010

1

tdcd

c

G

GD

Eqs (3)-(4) yield: mcc G )1(

where volume fraction of droplets in the air.

The total flux of the dissolved gas transferred by rain droplets:

Lcuqc

where u velocity of a droplet.

Page 10: T. Elperin, A. Fominykh and B. Krasovitov Department of Mechanical Engineering

where

Using Eqs. (3) and (6) we obtain :

,/ LtUT

(7)

tdcdcumqG

GDc

zq

tc c

2

2

Pe1

GGG CCTC

(8)

(9)

,/ DULPe ,)1( mumU

,12 CTCRHm gA

Ben-Gurion University of the NegevQueen Mary University of LondonIAAR Conference, Jerusalem

February 10, 2010

Equation of mass balance for soluble trace gas in the gaseous and liquid phases:

Combining Eqs. (3) (8) we obtain :

,)1(

2

mum

D

,Uuu GGGcccC 0,

Page 11: T. Elperin, A. Fominykh and B. Krasovitov Department of Mechanical Engineering

(11)

(12)

(13)

Ben-Gurion University of the NegevQueen Mary University of LondonIAAR Conference, Jerusalem

February 10, 2010

Boundary conditions :0T )(fC G

0 1GC

1

0

GC

where 1,0, Lz

Peclet number:

3161

43211

251

6.026PeGG

G

D

dc

dcmLD

DLU

(10)

]sm[130 121

1cwhere

Page 12: T. Elperin, A. Fominykh and B. Krasovitov Department of Mechanical Engineering

Fig. 1. Evolution of ammonia (NH3) distribution in the atmosphere due to scavenging by rain

Ben-Gurion University of the NegevQueen Mary University of LondonIAAR Conference, Jerusalem

February 10, 2010

Feingold-Levin DSD:

Fig. 2. Evolution of sulfud dioxide (SO2) distribution in the atmosphere due to scavenging by rain

Page 13: T. Elperin, A. Fominykh and B. Krasovitov Department of Mechanical Engineering

Ben-Gurion University of the NegevQueen Mary University of LondonIAAR Conference, Jerusalem

February 10, 2010

Fig. 3. Dependence of scavenging coefficient vs. altitude for ammonia wash out (linear initial distribution of ammonia

in the atmosphere) ( . 20,0, 10GGcgr cc

Fig. 4. Dependence of scavenging coefficient vs. altitude for ammonia wash out (linear initial distribution of ammonia

in the atmosphere) ( . 20,0, GGcgr cc

Scavenging coefficient:

Page 14: T. Elperin, A. Fominykh and B. Krasovitov Department of Mechanical Engineering

Fig. 5. Dependence of scavenging coefficient vs. rain intensity for ammonia

wash out at the early stage of rain (dimensionless time T = 5 . 104).

Fig. 6. Dependence of scavenging coefficient vs. rain intensity for ammonia wash out at the advanced stage of rain (dimensionless time T = 0.05).

Ben-Gurion University of the NegevQueen Mary University of LondonIAAR Conference, Jerusalem

February 10, 2010

Page 15: T. Elperin, A. Fominykh and B. Krasovitov Department of Mechanical Engineering

In this study we developed a model for scavenging of soluble trace gases in the atmosphere by rain. It is shown that gas scavenging is determined by non-stationary convective diffusion equation with the effective Peclet number that depends on droplet size distribution (DSD). The obtained equation was analyzed numerically in the case of log-normal DSD with Feingold-Levin parameterization.

It is demonstrated that scavenging coefficient for the wash out of soluble atmospheric gases by rain is time-dependent.

It is shown that scavenging coefficient in the atmosphere is height-dependent. Scavenging of soluble gas begins in the upper atmosphere and scavenging front propagates downwards with “wash down” velocity and is smeared by diffusion. It is found that scavenging coefficient strongly depends on the initial distribution of soluble trace gas concentration in the atmosphere. Calculations performed for linear distribution of the soluble gaseous species in the atmosphere show that the scavenging coefficient increases with the increase of soluble species gradient.

Ben-Gurion University of the NegevQueen Mary University of LondonIAAR Conference, Jerusalem

February 10, 2010