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Published byMarlene Anabel Moody Modified over 9 years ago
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Uncertainties in Wildfire Emission Estimates Workshop on Regional Emissions & Air Quality Modeling July 30, 2008 Shawn Urbanski, Wei Min Hao, Bryce Nordgren Missoula Fire Sciences Laboratory, US Forest Service
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Wildfire Fire Emission Inventories The Fire Sciences Laboratory has developed a MODIS- DB burned area algorithm to: Develop wildfire emission inventories for the western US Provide ‘rapid response’ wildfire emissions for air quality forecasting/management activities Demonstrate a prototype smoke dispersion – air quality forecasting system (assimilation of MODIS derived emissions for predicting fire impacts on regional air quality)
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Emission Estimate Method Fuel Loading Fire Information Meteorology Consumption Model Emission Factors Fuel Loading Land cover / fuel map Fuel loading model (vegetation load by fuel class) Meteorology – analysis / observations Fuel moisture (NFDRS) Consumption Model First Order Fire Effects Model (FOFEM) Fire Information MODIS-DB system (Missoula, MT) 4 daily observation per location Complete coverage of western US Combines active fire and burn scar detections – daily burned area at 1-km 2
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X = A * M *F C * EF X Mass emission of X over Δt : M (mass of fuel - dry vegetation) A ( area burned ) Fc ( fraction of fuel consumed ) EF ( emission factor X kg / kg fuel consumed) detection & area spatial & temporal distribution land cover map fuel loading model fuel consumption model meteorology fuel condition (moisture) fire average or phase specific cover type
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Uncertainties Associated with Land Cover and Fuel Loading Land Cover Fuel Characteristic Classifications System (FCCS) CONUS 1-km resolution 112 cover types USFS PNW Research Station, McKenzie (2007) FIA Forest Map CONUS 250-m resolution 138 SAF forest types Non-forested areas use FCCS USFS Forest Inventory & Analysis program and Remote Sensing Applications Center Fuel Loading Fuel Characteristic Classifications System (FCCS) FCCS fuel loading model Cross-walk to SAF forest types FOFEM Reference Database SAF/SRM cover types Cross-walk to FCCS USFS RMRS Missoula Fire Sciences Laboratory
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Uncertainties Associated with Land Cover and Fuel Loading CaseLand cover map Fuel loading AFCCSFOFEM BFCCS CFIAFOFEM DFIAFCCS Fuel loading uncertainty – Case A vs. Case B Map uncertainty – Case C vs. Case D
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Jan-06Jul-06Oct-06Apr-06Jan-07Jul-07Oct-07Apr-07 Monthly Burned Area Western US Burned area (km 2 ) 2000 6000 10000 0
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Jan-06Jul-06Oct-06Apr-06Jan-07Jul-07Oct-07Apr-07 Monthly CO Emissions Western US 1000 3000 5000 0 CO emissions (Gigagrams -CO)
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0 2000 10000 20062007 Annual CO Emissions by Fuel Method 6000 B A CDB A CD FUEL METHOD CO emissions (Gigagram) range ~20%range ~10% range in fuel consumption ~10% ~20%
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0 500 1500 20062007 Annual PM2.5 Emissions by Fuel Method 1000 B A CDB A CD FUEL METHOD PM 2.5 emissions (Gigagram) range ~20%range ~10%
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0 100 300 20062007 Annual NO X Emissions by Fuel Method 200 400 B A CDB A CD FUEL METHOD NO X emissions (Gigagram) range ~20%range ~5%
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0 50 250 20062007 Annual Methanol Emissions by Fuel Method 150 100 200 B A CDB A CD FUEL METHOD methanol emissions (Gigagram) range ~20%range ~10% NMVOC ~1-2% of C OVOC 60-70% of NMVOC
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0 300 20062007 Annual Formaldehyde Emissions by Fuel Method 100 200 B A CDB A CD FUEL METHOD formaldehyde emissions (Gigagram) range ~20%range ~10%
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2006 E_CO Metric ton-CO km -2 -270.0 - -168.0 -168.0 - -86.0 -86.0 - -34.0 -34.0 - -7.0 -7.0 - 11.0 11.0 - 52.0 52.0 - 157.0 157.0 - 400.0 400.0 - 850.0 Fuel Loading Impact on CO emissions Min = -266 Metric ton km -2 Max = +826 Metric ton km -2
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24.0 - 60.4 2006 E_PM2.5 Metric ton – PM2.5 km -2 -40.5 - -27.0 -26.9 - -13.1 -13.0 - -5.2 -5.1 - -1.1 -1.0 - 1.6 1.7 - 7.8 7.9 - 23.9 60.5 - 125.3 Fuel Loading Impact on PM2.5 emissions Min = - 41 Metric ton km -2 Max = +125 Metric ton km -2
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-0.1 - 0.6 2006 E_NO X Metric ton – NO X km - 2 -14.8 - -8.5 -8.4 - -3.5 -3.4 - -1.1 -1.0 - -0.2 0.7 - 2.3 2.4 - 5.6 5.7 - 11.4 11.5 - 23.7 Fuel Loading Impact on NO x emissions Min = - 15 Metric ton km -2 Max = +24 Metric ton km -2
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2007 E_CO Metric ton CO km -2 -545.6 - -332.1 -332.0 - -194.8 -194.7 - -99.0 -98.9 - -41.1 -41.0 - -9.2 -9.1 - 21.8 21.9 - 108.3 108.4 - 324.6 324.7 - 787.8 Land Cover Map Impact on CO emissions Min = - 546 Metric ton km -2 Max = +787 Metric ton km -2
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2007 E_PM2.5 Metric ton PM2.5 km -2 -82.8 - -50.4 -50.3 - -29.5 -29.4 - -15.0 -14.9 - -6.2 -6.1 - -1.4 -1.3 - 3.3 3.4 - 16.4 16.5 - 49.2 49.3 - 119.5 Land Cover Map Impact on PM 2.5 emissions Min = -83 Metric ton km -2 Max = +120 Metric ton km -2
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2007 E_NO X Metric ton NO X km -2 -15.6 - -9.3 -9.2 - -5.4 -5.3 - -2.9 -2.8 - -1.2 -1.1 - -0.3 -0.2 - 0.6 0.7 - 3.0 3.1 - 9.3 9.4 - 22.6 Land Cover Map Impact on NO x emissions Min = -16 Metric ton km -2 Max = +23 Metric ton km -2
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Summary Choice of land cover map and fuel model have significant impact on emission estimate Uncertainty in annual emissions for western US: 20% map and fuel model combined 10% map or fuel model alone Uncertainty varies spatially and temporally Large regional uncertainties e.g. 30% in MT and ID due to map choice alone, ~ 60% map and fuel model combined Don’t forget burned area, consumption model, & EF’s
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