Fuels For Schools General Air Quality Considerations Diane R. Lorenzen, P.E. Montana Department of Environmental Quality October 17, 2007.

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Presentation transcript:

Fuels For Schools General Air Quality Considerations Diane R. Lorenzen, P.E. Montana Department of Environmental Quality October 17, 2007

Air Quality Topics Emissions EstimatesEmissions Estimates –Criteria Air Pollutants –Hazardous Air Pollutants (HAPS) Is an Air Quality Permit Required?Is an Air Quality Permit Required? Ambient Air ImpactsAmbient Air Impacts Non-attainment AreasNon-attainment Areas

Criteria Air Pollutants Criteria Air Pollutants Regulated by Air Quality Standards Carbon Monoxide (CO)Carbon Monoxide (CO) Nitrogen Dioxide (NO 2 )Nitrogen Dioxide (NO 2 ) Sulfur Dioxide (SO 2 )Sulfur Dioxide (SO 2 ) Particulate Matter < 10 µm (PM 10 )Particulate Matter < 10 µm (PM 10 ) Particulate Matter < 2.5 µm (PM 2.5 )Particulate Matter < 2.5 µm (PM 2.5 ) Ozone, regulated as Volatile Organic Compounds (VOC)Ozone, regulated as Volatile Organic Compounds (VOC) Lead (Pb) [also a HAP]Lead (Pb) [also a HAP]

5 Criteria Pollutant Emissions Comparison Criteria Pollutant Emissions Comparison Potential to Emit (PTE) Tons of pollutant per year (tpy) 19 MMBtu/hr boiler (heat input) Pollu- tant WoodFuelDistillate Fuel Oil LP Gas (Propane) Natural Gas Fuel CoalFuel PM PM NOx SO < (unc) CO VOC Fuel 2 tons/hr 140 gal/hr 208 gal/hr 19,000 scf/hr 1 ton/hr

Example HAP Emissions Example HAP Emissions 2 MMBtu/hr Wood-fired Boiler HAP Emission Factor (lb/MMBtu) (1) Emission Rate (lb/hr) Emission Rate (tpy) Hydrogen Chloride* 1.9E Formaldehyde4.4E Benzene4.2E Acrolein4.0E Manganese1.6E Arsenic2.2E-054.4E (1) Emission Factors from AP-42, Section 1.6, External Wood Combustion

PM 10 Emissions Comparison Wood Burner Burner Size Heat Input PM 10 Emission Factor (lb/MMBtu) PM 10 Emissions (tpy) Small Wood Stove 18,000 Btu/hr Pellet Furnace 85,000 Btu/hr Outdoor Furnace 500,000 Btu/hr Typical FFS Boiler 2 MMBtu/hr Large FFS Boiler 19 MMBtu/hr Small Sawmill Boiler 32 MMBtu/hr Large Hog Fuel Boiler 292 MMBtu/hr

Boiler Stack and Buildings

Building Downwash

Ambient Air Quality Boundary Industrial Facility School Yard

Stack Height Considerations Minimize building downwash effectMinimize building downwash effect Good Engineering Practice Stack Height (GEP)Good Engineering Practice Stack Height (GEP) > 2.5 times adjacent building height

Sample Boiler Modeling Results

Non-Attainment Areas Wood Smoke is a primary contributor to PM2.5 impacts in Montana’s mountain valleys.

Locating a Project in a Non-attainment Area Contact state and local regulatory authorities at the beginning of planning Consider the effects of NAA restrictions on boiler operation and project economics

Source:

Open Burning vs. Fuel Boiler

Carbon Dioxide Source:

Burning Seasons in Montana Heating Season Open Burning Prohibited General Open Burning Fall Regulated Burning Fire Season JANFEBMARAPRMAYJUNJULAUGSEPOCTNOVDEC

Montana DEQ Air Quality Contacts Air permitting, emissions estimation and stack height: Deb Skibicki (406) Non-attainment Area information: Bob Habeck (406)