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ATMOSPHERIC
    DISPERSION
Muhammad Fahad Ansari
              12IEEM14
DEFINITION

Atmospheric Dispersion Modeling
is the mathematical simulation of
how air pollutants disperse in the
ambient atmosphere.
Plume’s centerline
             Z

                    Wind




      ΔH
                                                             H at X3


                                                                                 X
                                      H at X2

       h
                       H at X1


 y-
                                            H = Pollutant ’s release Hight
                                                H = h + ΔH


                                 y+         Hs = Actual release hight
Schematic Chimney                           ΔH = Plume rise
The model equation.
     We have selected the model equation in the form of
     presented by D.B. Turner. It gives:

     The ground level concentration X of pollutants at a
     point (x & y) downwind.
                     E               1 y 2       1 H 2 
χ( x , y ,0, H )   =            exp − ( )   exp − 2 ( )  
                    πs y s z u  
                                     2 s y  
                                                         sz 

              Where
               χ ( x , y ,0, H ) = Downwind concentration at ground level, g/m3
                     E = Emission rate of pollutant, g/sec
                    sy, sz = plumes standard deviations, m
                    x, y, z and H = distances, m
                    exp = e[ ] (exponential e, where e = constant and = 2.7182)
The value for the effective stack height is the sum of
the        physical        stack height (h) and the plume rise
⌂H.
                           H = h + ⌂H


      Where
               us d                              Ts − Ta  
                           1.5 +  2.68 ×10 ( P )
                                            −2
          ∆H =                                             d 
                                                               
                u                                Ts  
      Where
         us = stack velocity, m/sec
         d = stack diameter, m
         u = wind speed, m/sec
         P = atmospheric pressure, kPa
         Ts = Stack temperature, K (T oC + 273)
         Ta = air temperature, K

      Note: All these values depend upon the turbulent structure or stability of
            the atmosphere.
Means of Modeling

It  is   performed with computer
programs that solve the mathematical
equations    and    algorithms     which
simulate the pollutant dispersion.
ˆ   To predict the downwind concentration of air pollutants
    emitted from sources such as industrial plants and vehicular
    traffic.
r   To determine whether existing or proposed new industrial
    facilities are or will be in compliance with the National
    Ambient Air Quality Standards (NAAQS).
i   To assist in the design of effective control strategies to
    reduce emissions of harmful air pollutants.
   Meteorological conditions such as wind speed and direction, the
    amount of atmospheric turbulence (as characterized by what is
    called the "stability class"), the ambient air temperature and the
    height to the bottom of any inversion aloft that may be present.
   Emissions parameters such as source location and height,
    source vent stack diameter and exit velocity, exit temperature
    and mass flow rate.
   Terrain elevations at the source location and at the receptor
    location.
   The location, height and width of any obstructions (such as
    buildings or other structures) in the path of the emitted gaseous
    plume.

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Atmospheric dispersion im Muhammad Fahad Ansari 12IEEM14

  • 1. ATMOSPHERIC DISPERSION Muhammad Fahad Ansari 12IEEM14
  • 2. DEFINITION Atmospheric Dispersion Modeling is the mathematical simulation of how air pollutants disperse in the ambient atmosphere.
  • 3. Plume’s centerline Z Wind ΔH H at X3 X H at X2 h H at X1 y- H = Pollutant ’s release Hight H = h + ΔH y+ Hs = Actual release hight Schematic Chimney ΔH = Plume rise
  • 4. The model equation. We have selected the model equation in the form of presented by D.B. Turner. It gives: The ground level concentration X of pollutants at a point (x & y) downwind.  E   1 y 2    1 H 2  χ( x , y ,0, H ) =  exp − ( )   exp − 2 ( )   πs y s z u      2 s y      sz  Where χ ( x , y ,0, H ) = Downwind concentration at ground level, g/m3 E = Emission rate of pollutant, g/sec sy, sz = plumes standard deviations, m x, y, z and H = distances, m exp = e[ ] (exponential e, where e = constant and = 2.7182)
  • 5. The value for the effective stack height is the sum of the physical stack height (h) and the plume rise ⌂H. H = h + ⌂H Where us d    Ts − Ta   1.5 +  2.68 ×10 ( P ) −2 ∆H =  d   u    Ts   Where us = stack velocity, m/sec d = stack diameter, m u = wind speed, m/sec P = atmospheric pressure, kPa Ts = Stack temperature, K (T oC + 273) Ta = air temperature, K Note: All these values depend upon the turbulent structure or stability of the atmosphere.
  • 6.
  • 7.
  • 8. Means of Modeling It is performed with computer programs that solve the mathematical equations and algorithms which simulate the pollutant dispersion.
  • 9. ˆ To predict the downwind concentration of air pollutants emitted from sources such as industrial plants and vehicular traffic. r To determine whether existing or proposed new industrial facilities are or will be in compliance with the National Ambient Air Quality Standards (NAAQS). i To assist in the design of effective control strategies to reduce emissions of harmful air pollutants.
  • 10. Meteorological conditions such as wind speed and direction, the amount of atmospheric turbulence (as characterized by what is called the "stability class"), the ambient air temperature and the height to the bottom of any inversion aloft that may be present.  Emissions parameters such as source location and height, source vent stack diameter and exit velocity, exit temperature and mass flow rate.  Terrain elevations at the source location and at the receptor location.  The location, height and width of any obstructions (such as buildings or other structures) in the path of the emitted gaseous plume.