deriving biomass burning emissions from goes wildfire products
DESCRIPTION
Deriving Biomass Burning Emissions from GOES WildFire Products. P.I: Shobha Kondragunta NOAA/NESDIS/ORA Co-I: Chris Schmidt UW-Madison . NWS Air Quality Forecast Model Schematic. Emissions. Initial Conditions Boundary Conditions Meteorological Fields. Anthropogenic. - PowerPoint PPT PresentationTRANSCRIPT
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Deriving Biomass Burning Emissions from GOES WildFire Products
P.I: Shobha KondraguntaNOAA/NESDIS/ORA
Co-I: Chris Schmidt UW-Madison
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NWS Air Quality Forecast Model Schematic
Emissions
Anthropogenic Biogenic/Biomass Burning
Initial Conditions
Boundary Conditions
Meteorological Fields
Community Multiscale Air Quality (CMAQ) Model
Air Quality Forecast (O3, PM25,…)
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Problem
• PM25 emissions from biomass burning (forest fires) are currently not included in CMAQ simulations– This leads to uncertainties in PM25 forecasts during
long range transport of forest fire smoke
Long range transport of smoke (PM25) to US from forest fires in Canada during July 16-18, 2004
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Satellite Observations vs CMAQ PredictionsJuly 20 2004 16Z
Difference
Histograms
CMAQ model probably underestimating AOD fields due to absence of PM25 emissions from biomass burning
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GASP-CMAQ ComparisonsJuly 20 2004 16Z
Difference
Histograms
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Satellite vs Model (AOD Correlation)
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Model AOD vs Model PM25
• Model internally consistent
• Minimum threshold in CMAQ AOD
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Satellite AOD vs Model PM25
No correlation between satellite observed AOD and Model predicted PM25
Most of the observed smoke not represented in the model
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Solution: Incorporate PM25 emissions into CMAQ
Approach 1:Scale emission climatologies with fire counts (e.g., GOCART model)
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Solution: Incorporate PM25 emissions into CMAQ
Approach 1:Scale emission climatologies with fire counts (e.g., GOCART model)
Approach 2:Assume each fire point corresponds to 10 ha burning and emitting at a rate of 15 kg/ha/hr(e.g., HYSPLIT model)
Red 10 ug/m3
Orange 1 ug/m3
Yellow 0.1 ug/m3
Green 0.01ug/m3
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Solution: Incorporate PM25 emissions into CMAQ
Approach 1:Scale emission climatologies with fire counts (e.g., GOCART model)
Approach 2:Assume each fire point corresponds to 10 ha burning and emitting at a rate of 15 kg/ha/hr(e.g., HYSPLIT model)
Approach 3:Derive emissions using fire points, fuel load,and emission factors informationE=BA X FL X FF X EF
Red 10 ug/m3
Orange 1 ug/m3
Yellow 0.1 ug/m3
Green 0.01ug/m3
E = Emissions FF = Fuel Fraction
BA = Burned area EF = Emissions Factors
FL = Fuel Loading
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Approach 3 (Schematic)
Fire Counts (e.g., from GOES Vegetation
CMAQ
Fuel loadingFuel Fraction Consumed
Fuel type WeatherFuel moisture
Emissions Estimates
Emissions Factors
Static
Dynamic
Air Quality Forecast Model
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Summary and Work Plan
• Summary– CMAQ simulations during a known biomass burning event
underestimate PM25 and AOD fields. This is due to the absence of smoke emissions in the model
– Satellite-derived PM25 emissions in near real time will be developed to be incorporated into CMAQ
• Work Plan– Collect existing static (fuel load, emission factors) data bases
from USFS and other sources– Analyze and assess the databases– Derive emissions for a known fire episode (use GOES fire products
and other satellite information for fuel moisture and so forth)– Conduct impact studies in collaboration with USFS and EPA– Transition technology to NWS
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Acknowledgements
• CMAQ runs (Pius Lee and Jeff McQueen)• GOES AOD product (Ana Prados)• GOES re-gridded AOD product (Chieko
Kittaka)• HYSPLIT forecast map (Roland Draxler)