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Development and Application of a State-of-the-Science Plume-in-Grid Model CMAQ-APT

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Development of a new PiG model that uses the state-of-the-science for the host ... Crosswind plume resolution can be improved by using more puffs ... – PowerPoint PPT presentation

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Title: Development and Application of a State-of-the-Science Plume-in-Grid Model CMAQ-APT


1
Development and Application of aState-of-the-Scie
nce Plume-in-Grid ModelCMAQ-APT
  • Prakash Karamchandani, Christian Seigneur,
  • Krish Vijayaraghavan and Shiang-Yuh Wu,
  • AER, San Ramon, CA
  • Alan Hansen and Naresh Kumar
  • EPRI, Palo Alto, CA
  • CMAQ Workshop, October 2002

2
Plume-in-Grid Modeling
  • 3-D air quality models create an artificial
    dilution of stack emissions
  • lower concentrations of plume material
  • unrealistic concentrations upwind of stack
  • incorrect chemical reaction rates
  • incorrect representation of transport
  • Subgrid-scale representation of plumes can remove
    some or all of these major limitations

3
Previous PiG Models
  • Previous Plume-in-Grid (PiG) models include
    PARIS, URM, UAM-V, CAMx and CMAQ
  • All these PiG representations had limitations due
    to a simplified treatment of plume dispersion
    (empirical or first-order diffusion), simplified
    chemical mechanism in some cases and no effect of
    turbulence on plume chemistry

4
CMAQ-APT
  • Development of a new PiG model that uses the
    state-of-the-science for the host model (CMAQ)
    and the plume model (SCICHEM)
  • SCICHEM includes advanced treatments for plume
    dispersion (second-order diffusion) and chemistry
    (multistage mechanism, effect of turbulence)
  • CMAQ with Advanced Plume Treatment (APT)

5
Plume Dispersion
  • SCICHEM uses the SCIPUFF framework to simulate
    plume dispersion
  • A myriad of puffs is released from the source to
    represent the plume
  • Puffs are split when they become too large so
    that the effect of wind shear and turbulence on
    plume dispersion are properly characterized
  • Puffs that overlap are merged

6
Plume Chemistry
  • Plume chemistry is simulated with a chemical
    kinetic mechanism that evolves through three
    stages as the plume becomes dispersed into the
    background air (Karamchandani et al., 2000)
  • Effect of turbulence on plume chemistry can be
    simulated
  • Crosswind plume resolution can be improved by
    using more puffs
  • SCICHEM has been evaluated with plume data from
    SOS 95 and SOS 99

7
Evolution of Plume Chemistry
3
2
Long-range Plume Dispersion
Early Plume Dispersion
Mid-range Plume Dispersion
1
Reduced VOC/NOx/O3 chemistry acid formation
from OH and NO3/N2O5 chemistry
NO/NO2/O3 chemistry
Full VOC/NOx/O3 chemistry acid and O3 formation
8
SCICHEM/CMAQ Interface
Domain, grid information Geophysical
data Meteorological data Deposition velocities
Emissions, IC/BC
I/O API
I/O API
chemical concentrations
Models-3 CMAQ
SCICHEM
Point source emissions
I/O API
I/O API
Output concentrations and deposition
Output puff information
Dump puffs
chemical concentrations
9
Plume Dumping Criteria
  • Chemical criterion the plume has become
    chemically mature as determined by reaching the
    third stage of plume chemistry and a given
    threshold for the plume concentration ratio of O3
    / (O3 NO2)
  • Physical criterion the plume width must exceed
    the host model grid size

10
CMAQ-APT Application
  • Eastern United States with two nested grid
    domains (12 and 4 km resolution)
  • Episode of 11 to 15 July 1995
  • MM5 simulation of Seaman and Michelson (2000)
  • Thirty largest NOx point sources simulated with
    APT
  • Simulation with CMAQ and CMAQ-APT
  • CMAQ-APT is about 1.6 times slower than CMAQ for
    this simulation

11
CMAQ Surface O3 Concentrations13 July 1995, 3
p.m.
12 km domain
12
Effect of APT PiG Treatment onSurface O3
Concentrations13 July 1995, 3 p.m.
CMAQ-APT - CMAQ
12 km domain
13
Effect of Point Source NOx Emissionson Surface
O3 Concentrationswithout PiG Treatment
CMAQ - Background
12 km domain
14
Effect of Point Source NOx Emissionson Surface
O3 Concentrationswith APT PiG Treatment
CMAQ-APT - Background
12 km domain
15
CMAQ Surface HNO3 Concentrations13 July 1995, 3
p.m.
12 km domain
16
Effect of APT PiG Treatment onSurface HNO3
Concentrations13 July 1995, 3 p.m.
CMAQ-APT - CMAQ
12 km domain
17
Effect of Point Source NOx Emissionson Surface
HNO3 Concentrationswithout PiG Treatment
CMAQ - Background
12 km domain
18
Effect of Point Source NOx Emissionson Surface
HNO3 Concentrationswith APT PiG Treatment
CMAQ-APT - Background
12 km domain
19
Conclusions
  • CMAQ-APT provides an improved representation of
    the impact of large point sources
  • For isolated point sources, CMAQ-APT predicts
    less impact on O3 formation (up to 80 ppb less)
    and less impact on HNO3 formation (up to 24 ppb
    less)
  • CMAQ-APT has been subjected to a comprehensive
    beta-testing by three organizations
  • It will be applied to the California San Joaquin
    Valley for several CCOS episodes
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