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3 DIMENSIONAL DISPERSION MODEL

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Title: 3 DIMENSIONAL DISPERSION MODEL


1
3 DIMENSIONAL DISPERSION MODEL
  • Similar to heat conduction equation in 3-d
  • Solution for instantaneous release of X g of
    pollutant at t 0 and x y z 0

2
2-D Dispersion from a continuous, elevated point
source
3
  • The concentration profiles in the y and z
    directions look like Gaussian distributions (next
    3 slides)
  • By substituting
  • we get the standard double Gaussian
    distribution
  • Hence called the Gaussian plume equation

4
Figure 4-1 Wark Warner
  • Gaussian or normal distribution function

5
GAUSSIAN (NORMAL) DISTRIBUTION
6
DOUBLE GAUSSIAN DISTRIBUTION
7
DISPERSION COEFFICIENTS
  • Ky and Kz approximately proportional to wind
    speed
  • Ky/u and Kz/u approximately constant
  • ?y and ?z should vary approximately with
    x(1/2)
  • Field observations show more complex variation
    (Figures 6.7 and 6.8 de Nevers)
  • Wind speed and solar flux combine to give
    stability classes A - F (Table 6.1 de Nevers)

8
  • Horizontal dispersion coefficient

9
  • Vertical dispersion coefficient

10
Algebraic expressions for dispersion coefficients
  • The graphical representations of ?y and ?z can
    be approximated by algebraic expressions using
    parameters in Tables 4-1 through 4-3 of Wark,
    Warner, and Davis.

11
Algebraic representation of dispersion
coefficients Rural environment
12
Algebraic representation of dispersion
coefficients Urban environment
13
Algebraic representation of dispersion
coefficients Urban environment
14
GROUND LEVEL CONCENTRATION ALONG CENTER LINE
  • We are most interested in ground level, z0,
    concentrations (where humans and other life forms
    reside),
  • On the center line, y0, (where concentrations
    are at their maximum

15
2-D STEADY DISPERSION MODEL GROUND
REFLECTION
  • From the release height of H above ground,
    dispersion can progress upward towards the mixing
    height. In the downward direction the ground acts
    as a mirror unless the pollutant gets deposited.
  • The effect of the ground can be handled
    mathematically by treating the reflection as
    another point source located below ground (at - H)

16
Figure 4-3 Wark, Warner Davis
  • Use of an imaginary sourceto describe reflection
    at the ground

17
Figure 4-4 Wark, Warner Davis
  • Effect of ground reflection on pollutant
    concentration

18
MAXIMUM GROUND LEVEL CONCENTRATION
  • At z 0 (cwith reflection ) 2(cwithout
    reflection )
  • Not as simple at other z.
  • C(x,0,0) first increases with x due to ground
    reflection but horizontal dispersion (y
    direction) eventually decreases it. (Fig 4-5)
  • The location and magnitude of the maximum
    concentration can be determined from the
    equations above. Fig 4-8 provides a convenient
    tool. Other empirical methods are also available

19
Figure 4-5 Wark, Warner Davis
  • Concentration profiles along the center line of a
    stack plume

20
Figure 4-8 Wark, Warner Davis
  • Maximum Cu/Q value as a function of stability
    class and downwind distance

21
MIXING HEIGHT LIMITATION
  • As the ground represents a lower limit to the
    vertical dispersion, the mixing height represents
    an upper limit. Multiple reflections from the
    ground and the stable layer above need to be
    considered giving rise to
  • Approximation
  • No effect of mixing height for xltxL
  • Completely mixed in the z direction for xgt2 xL
  • Interpolate (on log-log plot) in between xL
    and 2 xL
  • xL corresponds to ?z0.47(L-H)

22
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23
ONE DIMENSIONAL SPREADING MIXING HEIGHT
LIMITATION
  • After a sufficient distance downstream (say ?z
    mixing height, xgt2xL) ?the plume can only
    disperse horizontally.
  • If we consider the plume well mixed in the
    vertical direction, we can obtain
  • where L mixing height
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