PURPOSE OF AIR QUALITY MODELING Policy Analysis

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Presentation transcript:

PURPOSE OF AIR QUALITY MODELING Policy Analysis Regional Planning Supplementary Control Systems / Air Quality Prediction System Emergency Preparedness / Accidental Releases Long Range Transport (Acid Rain) State Implementation Plan Revisions / New Source Review Prevention of Significant Deterioration ( PSD )

ATMOSPHERIC TRANSPORT Basic Mechanisms in the Movement of a Plume Advection Dispersion Treatment of Concentration Field Theoretical Approach Statistical theory Similarity theory K-Theory Models Higher Order Closure Models Experimental Approach Wind tunnel/ Water tank Field Studies (Expensive, Time Consuming & Limitation of Instrumentation )

TYPES OF AIR QUALITY MODELS Emission rate Modeling Ambient Air Concentration Modeling TYPES OF GROUND LEVEL CONCENTRATION MODELS Physical Model / Mathematical Model Historical Model Trend Model Prototype Model

BASIC SEGMENTS OF AN ELEVATED PLUME

BASIC SEGMENTS OF AN ELEVATED PLUME INITIAL PHASE Vertical Jet : Effluents are not deflected immediately upon entering the cross flow if (Vs / U > 4 ) Bent-Over Jet Section : Entrainment of the cross flow is rapid because by this time appreciable growth of vortices has taken place Thermal Section : Self generated turbulence causes mixing and determines the growth of plume TRANSITION PHASE Plume's internal turbulence levels have dropped enough so that the atmospheric eddies in the inertial sub range determines the plume's growth DIFFUSION PHASE The plume's own turbulence has dropped and energy containing eddies of atmospheric turbulence determine the growth of plume

DISPERSION OF HEAVY GASES Initial Acceleration Phase Initial Dilution Phase Slumping Phase ( internal buoyancy-dominated dispersion ) Transition Phase Passive Phase ( atmospheric turbulence-dominated dispersion )

TYPES Of PLUME TYPES OF PLUME RISE Continuos Plume: The release and the sampling time are long compared with the travel time Puff Diffusion / Instantaneous Plume: The release time or sampling time is short when compared with the travel time TYPES OF PLUME RISE Buoyancy Effect: Rise due to the temperature difference between stack plume and ambient air Momentum Rise: Rise due to exit velocity of the effluents (emissions)

Terms Used in Plume Rise Calculations PLUME RISE MODELS : Semi empirical equations based on heat flux, Analytical solutions and Numerical models. Terms Used in Plume Rise Calculations Buoyancy Flux (F) Momentum Flux (Fm):

STABILITY PARAMETER where, g = Acceleration due to gravity Vs = Stack exit velocity d = Exit gas diameter Ts = Stack gas exit temperature Ta = Ambient air temperature STABILITY PARAMETER = Ambient potential temperature gradient

ANALYTICAL SOLUTIONS MOMENTUM SOURCES for Unstable and neutral conditions for stable conditions The lower value of the above equations is used for the concentration calculations.

ANALYTICAL SOLUTIONS BUOYANT PLUMES for Unstable and Neutral conditions Dh(x) = Const. F1/3 Us-1 x2/3 x* = 14 F 5/8 when F < = 55 m4/sec3 x* = 34 F 2/5 when F > 55 m4/sec3 3.5x* = Downwind distance to the point of final rise for stable conditions The distance to final rise is given by xf = (2.0715 * Us) / S 0.5

BUOYANT PLUMES for Calm Conditions for wind speeds < 1 m/sec

JETS The plume rise for a jet is computed as follows: Dh = 4.0 Fm 1/4 S -1/4 Determination of the Type of Plume (Momentum or Buoyant) Crossover Temperature (DTc) Unstable or Neutral case Buoyancy rise if DT >= DTc or is assumed to be Momentum Stable case The above calculations are valid for cases with stack exit temperature Ts greater than or equal to ambient temperature Ta.

SEMI-EMPIRICAL EQUATIONS Most of the plume rise equations in this category are based on the following equations where, Qh is the heat emission rate of the source Qh = Qm Cp (Ts - Ta) Qm is the total mass emission rate Qm = (p/4) ρs d2 Vs

NUMERICAL MODELS Conservation of Mass Conservation of Moisture Conservation of Energy (Heat) Conservation of Momentum

NUMERICAL MODELS Conservation of Horizontal Momentum Conservation of Solid Particles

Relationship between Plume Rise z, Downwind Distance x and Time t Hydrostatic Environment - No Liquid or Solid Particulate Matter Assumptions made in developing the above equations Boussinesq approximation has not been used Solid body effects are included only in the horizontal direction Downwash is neglected during computations i.e. We = 0

Stack Exit Velocity 20.00 m/sec Stack Exit Temperature 1000.00 ° K PLUME RISE 1 Stack Diameter 2.24 m Stack Height 61.00 m Stack Exit Velocity 20.00 m/sec Stack Exit Temperature 1000.00 ° K Atmospheric Temperature 281.00 ° K Emission Rate 348.26 g/sec Wind Speed at stack height 5.70 m/sec Calculate plume rise for stable, unstable and neutral atmospheric conditions.

Procedure for Problem 1 Calculate F Calculate DTc Decide buoyancy/momentum/calm Choose the plume rise equation Calculate Dh

PLUME RISE 2 The wind and stack gas spreads are 3 m/sec at 10 m and 6 m/sec, respectively. The stack diameter is 2 m. The atmospheric condition is near neutral with an average temperature of 300 ° K. The stack gas temperature is 450 ° K. Estimate plume rise. (hs = 50 m)

FLARE STACK Flare Length as per API L = 0.006 Q0.478 where, L = Flare length (ft) Q = Flared gas heat release (BTU/hr) Vertical Height of Flame hfv = L Sin q q = 45 ° Plume Rise He = hs + hfv + Dh