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Published byKelley Simpson Modified over 8 years ago
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June 15, 2011 Bob Dulla Sierra Research
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Fairbanks PM 2.5 Modeling Domain – Grid 3 2
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Fairbanks PM 2.5 Nonattainment Area 3
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Draft Emission Estimates by Source (Winter 2008) Fine Particulates (PM 2.5 ) Sulfur Dioxide (SO 2 ) 4
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Fairbanks Grid 3 2007/2008 Oct-Mar Emissions by Source Sector (tons/day) SourcePM 2.5 SO 2 NOXVOCNH 3 CO Point0.397.0713.030.500.457.24 Area1.823.281.903.620.0014.13 On-Road0.180.039.533.410.2965.70 Non-Road0.100.000.094.470.0011.71 Total2.4910.3924.5511.990.7498.78 5
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Studies Conducted to Improve Fairbanks Emission Estimates Telephone survey of space heating by zip code Space heating appliance survey Laboratory measurements of vehicle emissions Wood storage and drying time Survey of emissions from each point source in the area Laboratory measurements of emissions from fuels used in Fairbanks homes 6
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Residential Heating Device and Fuel Surveys for Fairbanks Winter Main Purposes: Determine an accurate mix of heating devices and fuels to estimate PM 2.5 for Fairbanks. Surveys conducted for 2006, 2007, 2010 and 2011 2011 Survey sample size of 712 respondents Six zip codes: 99701, 99703, 99705, 99709, 99712, 99775 626 landline (apportioned by zip code population) 86 cell phone (randomly selected) Key questions answered Device counts Device and fuel usage Device and fuel properties Home heating costs Regional and sub-regional variations 7
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2011 Home Heating Survey Device Counts StatisticParameterSurvey Results Total Estimated Devices for Fairbanks Wood 8,62322.53% Central Oil 20,26552.70% Portable 1,2942.95% Direct Vent 4,63510.80% Natural Gas 1,0062.60% Coal Heat 3590.82% District Heat 7552.22% Electric Device 6831.62% Other 1,5093.75% Total 39,129100% 8
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Summary of 2006, 2007, 2010 and 2011 Home Heating Surveys StatisticParameter Survey Results 2006200720102011 Average Winter Device Use by Type (% of Household Use) Wood10.1%11.8%17.2% 14.8% Central Oil68.0%63.6%67.3% 68.0% Portable0.7%0.5%0.2% 0.9% Direct Vent8.6%7.4%8.2% 9.2% Natural Gas2.6%2.3%4.5% 3.3% Coal Heatn/a 0.5% 0.6% District Heat2.8%1.1%1.3% 1.9% Electric Devicen/a 0.5% Other7.2%13.4%0.7% 0.9% 9
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Space Heating Appliance Survey CCHRC pilot study of 12 homes – Feb/Mar 2010 Larger study of 30 homes – Dec 2010/Jan 2011 Instrumentation and data logs used to measure fuel use and/or stack temperatures for fuel oil only wood only wood and fuel oil Firewood samples collected to determine moisture content 10
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Summary of Firewood Cure Adequacy 11
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Pilot Study – Diurnal Profile of Mixed Oil-Wood Heating Use 12
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Characterizing Vehicular Contributions to PM 2.5 in Fairbanks in Winter Main Purposes: Determine Effect of Plugin and Temperature on PM 2.5 Emissions, Compare Results with EPA’s MOVES Model 6-vehicle pilot study in 2009-10, developed and tested methods, upgraded facility Main study Jan/Mar 2011 measured exhaust emissions from 11 cars & 22 light duty trucks, MYs 1983-2010 Fairbanks Cold Temperature Test Facility (temps from -30 to 44°F) Dyno tests with plugin and twice w/o plugin (different temps.) Cold start Alaska Drive Cycle with 5-minute warmup idle and hot start ADC, monitored engine temperatures Sponsors: DEC with support from FNSB 13
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PM 2.5 Emissions for Composite Trip (4.74 mi) (ADC Testing versus EPA MOVES Model) 14
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Aircraft Emissions Activity data collected for major airports (FAI, Wainwright & Eielson) Separate emission estimates computed for aircraft and GSE 6 modes of operation/LTO (emitted at different heights) Challenge to correctly allocate to WRF vertical layers Vast majority of pollutants emitted at ground level SMOKE treats airport emissions as point source Magnitude of emissions from combined airports trivial for non-CO 2 pollutants (fraction of a metric ton/day) 15
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Rail Emissions ARRC provided activity data for line-haul and yard operation separately Line-haul activity for individual line segments (e.g., Healy to Fairbanks) average # of trains/day for each winter month hours of operation provided (e.g., 0800 – 1600) average fuel use per train Separate estimates of fuel use for Fairbanks and Eielson yards Total rail NOx is ~ 1 ton/day, max grid cell value is 1.2 lbs/day 16
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Firewood Storage Best Practices CCHRC cut fresh trees in the spring and fall of 2010 Measured initial moisture levels for spruce, birch and aspen Set up several wood storage/preparation methods (shed, stacked/tarp, uncovered/stacked & solar kiln) Collected regular moisture measurements to monitor curing Discontinued measurements when moisture reached 20% or less 17
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Firewood Storage Best Practices (cont.) Key findings from spring harvest: Split firewood dries more quickly than whole logs Most storage methods produced moisture levels ≤ 20% in 6-week to 3-month summer period Whole logs had moisture levels between 21% - 43% by late August Key findings from fall harvest: Firewood dries marginally over the winter Moisture levels by late March between 40% - 72% Firewood harvested in the fall should not be burned the following winter 18
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Other Studies ADEC requested information on winter hourly emissions from each point source located in the Fairbanks area All sources responded Data is currently being processed Borough contract with OMNI Labs to measure emissions from following using Fairbanks fuels, but not Fairbanks winter temperatures – results pending Wood stoves Pellet stoves Coal stoves OWBs – with/without add-on stack controls (e.g., catalyst) Fuel oil stoves (with #1 & 2 heating oil & used motor oil) 19
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Emission Inventory Changes Expected Wood burning emissions will increase Motor vehicle emissions will decrease Diurnal profiles from most sources will be improved Chemical profiles for space heating fuels will be more representative Borough fuels 20
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