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Comprehensive Particulate Matter Modeling: A One Atmosphere Approach

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A Hybrid Method for Particulate Matter Source Apportionment: Using A Combined Chemical Transport and Receptor Model Approach Yongtao Hu, Sivaraman Balachandran, Jorge ... – PowerPoint PPT presentation

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Title: Comprehensive Particulate Matter Modeling: A One Atmosphere Approach


1
A Hybrid Method for Particulate Matter Source
Apportionment Using A Combined Chemical
Transport and Receptor Model Approach
Yongtao Hu, Sivaraman Balachandran, Jorge
Pachon,Jaemeen Baek, Talat Odman, James A.
Mulholland and Armistead G. Russell School of
Civil and Environmental Engineering, Georgia
Institute of Technology, Atlanta, Georgia
Currently at Currently at IIHR-Hydroscience and
Engineering, University of Iowa. Iowa City, Iowa

10th Annual CMAS Conference, October 25th, 2010
Georgia Institute of Technology
2
Objective and Approach
  • Develop a source-based approach to integrating
    receptor- and source- oriented modeling of
    particulate matter
  • Improve source impact estimates
  • Extend impact quantification to more sources
  • Expanded spatial and temporal coverage of source
    apportionment
  • Provide estimates of uncertainties for spatial
    analysis
  • Approach
  • CMAQ DDM3D/PM to provide initial source impacts
    and sensitivities
  • Use sensitivities to adjust source impacts using
    CMB-type formulation
  • Use adjustments and species performance to assess
    uncertainties
  • Application
  • One month simulation over CONUS
  • STN monitors
  • Six cities

Georgia Institute of Technology
3
Receptor Oriented Modeling (RM)
  • RM approaches such as CMB rely on using observed
    concentrations of the PM composition at a
    receptor, along with knowledge of the composition
    of source emissions (source profiles), to solve a
    species balance equation that estimates the
    source impacts. For example CMB species balance
    equations
  • Limitations/assumptions/uncertainties
  • Emission compositions are constant and known (not
    good for some sources)
  • No reactions or differential phase changes (not
    bad for many, but not all, primary compounds)
  • Most sources are included (typically only about
    80 of mass is)
  • Source compositions are linearly independent of
    each other (co-linearity can be a problem)
  • The number of sources is less than or equal to
    chemical species (limitation)

total number of emission sources considered
measured concentration of species i
RMs prediction error to be minimized
emission fraction of species i in total PM2.5
emitted from source j
source js impact on the total PM2.5 concentration
Georgia Institute of Technology
4
Source-Oriented Modeling (SM)
  • SM approaches using chemical transport models
    (CTMs) follow a first principles approach,
    tracking the emissions, transport, transformation
    and loss of chemical species in the atmosphere to
    simulate ambient concentrations and source
    impacts. For example using DDM3D derived
    sensitivities
  • Limitations/uncertainties
  • Emissions estimates, Meteorological inputs,
    Missing processes and parameter uncertainties
  • Benefits
  • Large number of sources, direct link to sources,
    spatial coverage, non-linear chemistry

total number of emission sources that included in
CTM
calculated sensitivity coefficients of species
is concentration to emissions from source j
Simulated concentration for species i
impact from source js emissions outside of the
domain
estimate of source js impact on species is
concentration
impact from source js emissions prior to the
simulation period
total emissions of all tracked pollutants emitted
from source j
Georgia Institute of Technology
5
A hybrid approach for particulate matter source
apportionment Combining receptor modeling with
chemical transport modeling
Limited number of sources vs. completeness of
source categories
SMs prediction error to be minimized
Sensitivities to emissions
Sensitivity to BC
Sensitivity to IC
Constraints from source profiles upgraded to
constraints of source-receptor relationship
derived from CTM
We modify the species balance equations which CMB
is based to use outputs of the CTM.
Georgia Institute of Technology
6
Hybrid Approach (continued)
The hybrid approach relies on minimizing the
differences (c2) between CTM-calculated and
observed PM2.5 concentrations (including each
PM2.5 component and metals) while considering
estimated uncertainties in both the observations
and source emission rates
where
So,
CTM-simulated base case impact of source j on
species i
to weigh the amount of change in source strengths
total number of sources
total number of species
ratio of adjusted impact from source j to the
base case
a priori uncertainties
Instead of the original CMB solution
Georgia Institute of Technology
7
Application
  • 2004 MM5-SMOKE-CMAQ-DDM3D simulation
  • 36-km grid covering continental United States as
    well as portions of Canada and Mexico.
  • Projected VISTAS emissions inventory used as a
    priori inventory.
  • First order DDM sensitivity coefficients
    calculated for 32 separate source categories.
  • Ambient PM2.5 concentrations apportioned to the
    32 separate sources
  • STN, IMPROVE, SEARCH and ASACA networks
  • TOT measurements of OC and EC from STN and ASACA
    converted to TOR equivalences.

Georgia Institute of Technology
8
PM2.5 monitoring networks
Georgia Institute of Technology
9
Hybrid Approach Applied at STN sites
  • Major PM2.5 ions and metals measured
  • Use reported detection limits and measurement
    uncertainties
  • Obtain metals sensitivities to sources
  • Split using source specific PM2.5 (unidentified
    portion) sensitivity coefficients and source
    profiles of metals for each of the 32 categories
    assuming that metals remain intact from source to
    receptor.
  • Source profiles are assembled from the 84
    profiles compiled by Reff et al. 2009 EST. The
    profiles split PM2.5 emissions to the above 42
    species.

Georgia Institute of Technology
10
Choice of ? for Ridge Regression
?N/J42/321.3125 selected
11
CMAQ/Hybrid Concentrations
Georgia Institute of Technology
12
Initial/Refined (CMAQ/Hybrid) difference (?2Ci)
between simulated and observed PM2.5
concentrations
Georgia Institute of Technology
13
Initial and Refined PM2.5 source impacts (in
percentage)
Woodstove
Solvent
Others
Prescribed burn
Other combustion
Nonroad diesel
On-road gasoline
Natural gas combustion
Mineral product
On-road diesel
Fuel oil combustion
Meat cooking
LPG combustion
Dust
Waste burn
Metal product
Coal combustion
Livestock
Biogenic
Aircraft
Georgia Institute of Technology
14
Major contributing sources in six cities
Georgia Institute of Technology
15
Initial/Refined (CMAQ/Hybrid) Source Impacts
Georgia Institute of Technology
16
Initial/Refined (CMAQ/Hybrid) Source Impacts
Georgia Institute of Technology
17
Compare with the CMB Results
  • CMB apportionment allowed resolution of less than
    10 sources while the hybrid method resolved 32,
    and included total contributions from both
    primary and secondary paths.
  • In order to do more specific comparisons, the
    hybrid results are re-grouped to match up with
    the CMB categories by
  • (1) splitting the primary and the secondary
    contributions from each hybrid category, using
    the source specific composition profiles and
    assuming that the primary species are inert and
    stick together, and
  • (2) merging the hybrid sub-categories that split
    to primary and secondary portions to the major
    categories that match up with the CMB sources.

Georgia Institute of Technology
18
Initial/Refined (CMAQ/Hybrid) Source Impacts
Georgia Institute of Technology
19
Initial/Refined (CMAQ/Hybrid) Source Impacts
Georgia Institute of Technology
20
Initial/Refined (CMAQ/Hybrid) Source Impacts
Georgia Institute of Technology
21
Benefits and Future Work
  • Hybrid Approach Benefits
  • Completeness of sources
  • More complete range of sources quantified
  • First principles constraints
  • Can account for non-linearities and secondary PM
    sources
  • Limitations removed, for spatial and temporal
    applications.
  • Uncertainty estimation
  • Ongoing Work
  • Source apportionment at IMPROVE, ASACA and SEARCH
    sites.
  • Simulating full year.
  • Further uncertainty estimation.
  • Additional approach for inverse modeling
  • Optimize source compositions.
  • Interpolation of source impacts spatially and
    temporally
  • Increased resolution

Georgia Institute of Technology
22
Acknowledgements
  • EPA funding under grants R83362601 and R83386601
  • Southern Company and Georgia Power

Georgia Institute of Technology
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