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Chapter 5 Dispersion Models

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A source is emitting pollutant stack gas from its stack of 100m. ... 5 km North (N) of the source if the wind blows from SouthWest (SW) direction. ... – PowerPoint PPT presentation

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Title: Chapter 5 Dispersion Models


1
Chapter 5 Dispersion Models
  • 5.1 Dispersion of pollutants in the atmosphere
  • 5.2 Models
  • 5.3 Gaussian Dispersion Model
  • 5.4 Effective stack height
  • 5.5 Area and line sources

2
Introduction
  • Connection between Source and Atmosphere
  • Emissions of pollutants from sources
  • Air quality in the atmosphere
  • Emission ?Air Quality (Imission)
  • Connection MODELS
  • Very wide variety of models

3
What is MODEL?
  • A mathematical relation (equation or a set of
    equations) to estimate some parameter(s) (i.e.
    Outputs) by using some other set of parameter(s)
    (i.e. Inputs)

MODEL Yj f(Xi)
Output(s), Yj
Input(s), Xi
4
MODELS
  • Deterministic ModelsInitially KNOWN relationship
    between inputs and outputs
  • Box Models (Simple Box Model, Eulerian Box
    Model, Lagrangian Box Model) Receptor
    Models Dispersion Models

5
MODELS
  • Stochastic Models
  • Initially UNKNOWN relationship between inputs
    and outputs
  • Mathematical approximations such as polynomial
    equations, neural networks, fuzzy networks etc

6
General Structure of Air Pollution Models
7
Detailed Structure of Atmospheric Chemical
Transport Models
8
Parameters in Models
  • Source Parameters (Emission Characteristics) Emis
    sion rates of pollutants (mass/time) Physical
    location of source Temperature of gas
    release Plume Rise
  • Meteorology Atmospheric temp. Atmospheric
    stability (needed for Dipersion coefficients)
    Wind velocity
  • Atmospheric Chemistry Chemical Reaction in the
    atm. Depositions (wet or dry)
  • Surface Parameters Surface geometry, roughness,
    seas, urban or rural areas etc

9
Scope of this Chapter
  • Dispersion Models
  • GAUSSIAN DISPERSION MODEL

10
Theory Behind Gaussian Dispersion Model (GDM)
  • A Mass Balance on the basis of a specific
    pollutant In a Control Volume
  • Accumulation Rate (mass/time)
  • All Flows In
  • All Flows Out
  • Formation Rate
  • - Destruction Rate

11
Theory Behind Gaussian Dispersion Model (GDM)
Inputs
Diffusion
Outputs
Advection (by wind)
  • Two main transportation mechanisms are involved
  • Diffusion on molecular basis in all directions
    (i.e.in x, y and z directions)
  • Transportation by wind in only wind direction
    (i.e. in x direction)

12
Theory Behind Gaussian Dispersion Model (GDM)
  • Molecular diffusion

  • (Ficks Law)
  • Nx Mass diffusion flowrate of gas pollutant in
    x direction (mass/time)
  • Dx Diffusivity (turbulent mixing coefficient)
    in x direction (area/time)
  • C Concentration (mass / volume)
  • A Cross-sectional area (Adydz) in the
    direction of transportation (i.e. x direction)

13
Theory Behind Gaussian Dispersion Model (GDM)

Ci concentration of pollutant i, µg/m3 u
mean convective velocity in x-direction (wind
velocity), m/sec dy mean convective velocity
in y-direction, m/sec dz mean convective
velocity in y-direction, m/sec Dx mass
diffusivity in x-direction, m2/sec Dy mass
diffusivity in y-direction, m2/sec Dz mass
diffusivity in z-direction, m2/sec F pollutant
removal or accumulation rate, µg/sec
14
Theory Behind Gaussian Dispersion Model (GDM)
Dividing both sides by control volume dxdydz
Assuming mass diffusivities are constant due to
continuity principle, that is
15
Theory Behind Gaussian Dispersion Model (GDM)
  • Last equation becomes
  • Basic dispersion equation
  • We need to evaluate Gaussian Dispersion mechanism
    to further go on

16
Gaussian Dispersion Mechanismin 2D
17
Gaussian Dispersion Mechanismin 3D
18
Gaussian Dispersion Mechanism
  • In order to obtain Gaussian Model, we need to
    simplify the Basic dispersion Equation
  • Assumptions
  • Pollutant emission rate (Qi) from the source is
    constant
  • Wind velocity in y and z directions is zero
  • Wind velocity in x direction is constant
  • Advective transportation is dominant over
    diffusion in x direction

19
Gaussian Dispersion Mechanism
  • Pollutant accumulation or removal is zero
  • F0
  • With all these assumptions Basic Eqn
  • Becomes a second order differential eqn

20
Gaussian Dispersion Mechanism
  • Solution
  • K is an indefinite integration constant
  • To find K we need to determine the integration
    limits depending upon the dispersion geometry.
  • In the plume we have

21
Gaussian Dispersion Mechanism
  • Integration limits for a ground source
  • y -infinity to infinity
  • z 0 to infinity
  • Result
  • K is

22
Gaussian Dispersion Mechanism
  • Inserting into main eqn
  • By definition we have the following relations
    between diffusion and dispersion coefficients
  • Inserting them into main eqn,we have
  • Gauss Dispersion Eqn for ground level source

23
Concepts about GDM
  • Ground Level Source

24
Concepts about GDM
  • Stack Dip Downwash
  • If
  • Stack dipdownwash is neglected
  • Otherwise Reduced Stack height

25
Concepts about GDM
  • Plume Orientation

26
Concepts about GDM
  • Elevated source

27
Concepts about GDM
  • Ground Reflection

28
Concepts about GDM
  • Ground Reflection
  • (Vertical Concentration profile)

29
Concepts about GDM
  • Ground Reflection
  • (Horizontal concentration change)

Cmax and its location (xmax) is important
30
Most General Form of GDM
  • Terms in GDM

31
Plume Shapes depending on Stability
32
Plume Shapes depending on Stability
33
Plume Shapes depending on Stability
34
Plume Shapes depending on Stability
35
Plume Shapes depending on Stability
36
Plume Shapes depending on Stability
37
How to use GDM?
  • Need to know proper orientations of both Source
    and ReceptorSource at (0,0,H) and Receptor at
    (x,y,z) ?C(x,y,zH)
  • Pollutant Emission Rate from source Q (mass of
    pollutant/time) NOT Volume flowrate of
    Stackgas
  • Atmospheric Stability Category (A, B, C. etc.)
  • Wind velocity at stack height u
  • Dispersion Coefficients sy and sz
  • Effective Stack height H hs ?h ?
    Calculation of Plume rise (?h )
  • THEN USE GDM ? C(x,y,zH) .

38
Source-to-Receptor Orientation
  • A source is emitting pollutant stack gas from its
    stack of 100m. Define the location of a ground
    level receptor site 5 km North (N) of the source
    if the wind blows from SouthWest (SW) direction.
  • ?Draw the geographical orientation of source and
    receptor and calculate x, y and z coordinates
    for GDM.

39
  • Solution

Distance x (5 km) Cos 45
40
Receptor-to-Source Orientation
  • A park area is located in 10 km west (W) of a
    thermal power plant having 200m tall stack.
    Determine the geographical positions of receptor
    and source points if the wind blows from
    East-NorthEast (ENE) direction.
  • ?Draw the geographical orientation of source and
    receptor and calculate x, y and z coordinates
    for GDM

41
  • Solution

42
Dispersion Coefficients sy, sz
As plume goes away from source, dispersion
increases in both y and z directions ? As x
increases ? sy and sz icrease depending upon
stability
43
Dispersion Coefficients sy, sz
  • First developed graphical representations

sy
sz
44
Dispersion Coefficients sy, sz
  • Mathematical simulations for Disp. Coeffs.

45
Calculation of Plume Rise (?h)
46
Calculation of Plume Rise (?h)
47
Calculation of Plume Rise (?h)
48
Calculation of Plume Rise (?h)
49
Calculation of Plume Rise (?h)
  • Parameters in Briggs Equations

50
EXAMPLES
51
EXAMPLES
52
EXAMPLE
53
Graphical representation of concentration versus
x distance
54
Ground Level Max Concentration and Location
  • Turners Graphical Solution
  • A Graph for
  • Cu/Q versus xmax
  • Max Concentration depends on
  • Stability category
  • Effective stack height
  • GRAPH

55
(No Transcript)
56
Analytical Solution for Cmaxvalid for all
stability categories
57
Analytical Solution for Cmaxvalid only for
Slightly stable and Neutral conditions
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