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Modeling of Ammonia and PM 2.5 Concentrations Associated with Emissions from Agriculture. Megan Gore, D.Q. Tong, V.P. Aneja, and M. Houyoux Department of Marine, Earth & Atmospheric Sciences North Carolina State University Raleigh, NC 27695 7th Annual CMAS Conference October 6-8, 2008.
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Modeling of Ammonia and PM2.5 Concentrations Associated with Emissions from Agriculture Megan Gore, D.Q. Tong, V.P. Aneja, and M. Houyoux Department of Marine, Earth & Atmospheric Sciences North Carolina State University Raleigh, NC 27695 7th Annual CMAS Conference October 6-8, 2008
Outline • Introduction – Ammonia in North Carolina (NC) • Model Configuration • Preliminary Results • O3, NH3,PM2.5, NH4+ • Conclusions • Future Work NH3
Why do we care about Ammonia? Elevated levels of NHx (=NH3 + NH4+) can lead to: • Nitrogen enrichment and eutrophication in aquatic ecosystems • Impacts on crop and forest production • Particulate matter (PM) formation • Visibility degradation • Odor
Nitrogen Emissions in N.C. • NH3 Agricultural Sources • Total ~ 40% of Nitrogen • 138,843 NH3 tons/yr • Swine 68,540 (49%) • Cattle 24,952 (18%) • Broilers 13,669 (10%) • Turkeys 16,486 (12%) • Fertilizer 8,720 (6%) • Other 6,476 (5%) • (Aneja et al., 1998)
Ammonia Atmospheric Chemistry Atmospheric Reactions: • NH3(aq) + H20 NH4OH(aq) • NH3(g) + H2SO4(aq) NH4HSO4(aq) • NH3(g) + NH4HSO4(aq) [NH4]2SO4(s or aq) • NH3(g) + HNO3(g) NH4NO3(s or aq) • NH3(g) + HCl(g) NH4Cl(s or aq) • NH3(g) + OH·(g) N·H2(g) + H2O(g)
Model Configuration • Model: Community Multi-Scale Air Quality (CMAQ)Model • Episode: January 1 – December 31, 2002 • Domain: Continental U.S., N. Mexico, S. Canada 36 km, 24 layers • Meteorology: MM5 - Pleim-Xiu Land Surface module on • Emissions: 2002 National Emissions Inventory • I/B Conditions: MOZART-2 for lateral BC • Gas-phase mechanism: Carbon Bond (CB05) • Aerosol module: AE4
space Preliminary Results Ozone January Base Run – Ozone Monthly Average January Reduced Run* – Ozone Monthly Average ppbv *Reduced Run – NH3 Emissions turned off
Preliminary Results Ozone July Base Run – Ozone Monthly Average July Reduced Run* – Ozone Monthly Average ppbv *Reduced Run – NH3 Emissions turned off
Preliminary Results – NH3 January Base Run – NH3 Monthly Average January Reduced Run* – NH3 Monthly Average ppbv *Reduced Run – NH3 Emissions turned off
Preliminary Results – NH3 July Base Run – NH3 Monthly Average July Reduced Run* – NH3 Monthly Average ppbv *Reduced Run – NH3 Emissions turned off
Preliminary Results PM2.5 January Base Run – PM2.5 Monthly Average January Reduced Run* – PM2.5 Monthly Average *Reduced Run – NH3 Emissions turned off
Preliminary Results PM2.5 Base Run – January 2002, NC Monthly Average
Preliminary Results PM2.5 Reduced Run – January 2002, NC Monthly Average
Preliminary Results PM2.5 July Base Run – PM2.5 Monthly Average July Reduced Run* – PM2.5 Monthly Average *Reduced Run – NH3 Emissions turned off
Preliminary Results PM2.5 Base Run – July 2002, NC Monthly Average
Preliminary Results PM2.5 Reduced Run – July 2002, NC Monthly Average
Preliminary Results–NH4+ Aerosol January Base Run – NH4+ Monthly Average January Reduced Run – NH4+ Monthly Average *Reduced Run – NH3 Emissions turned off
Preliminary Results–NH4+ Aerosol July Base Run – NH4+ Monthly Average July Reduced Run – NH4+ Monthly Average *Reduced Run – NH3 Emissions turned off
Conclusions • Agricultural NH3 emissions have a significant impact on PM2.5 and NH4 aerosol predicted concentrations
Future Work • Additional model runs turning off emissions from the various agricultural sectors • Evaluate the effect of ammonia emissions of aerosol composition • Model evaluation using observed values of pollutants • Meteorological analysis
Acknowledgements • USDA • USEPA • NCSU Air Quality Research Group
Atmospheric emissions, transport,transformation & deposition of trace gases *Indirect deposition is direct deposition to land followed by runoff or seepage through groundwater to a surface water body.
Preliminary Results Ozone Base Run – January 2002, NC Monthly Average ppbv
Preliminary Results Ozone Reduced Run – January 2002, NC Monthly Average ppbv
Preliminary Results Ozone Difference Between Base Run and Reduced Run January 2002, NC - Monthly Average ppbv
Preliminary Results Ozone Base Run – July 2002, NC Monthly Average ppbv
Preliminary Results Ozone Reduced Run – July 2002, NC Monthly Average
Preliminary Results Ozone Difference Between Base Run and Reduced Run January 2002, NC - Monthly Average ppbv
Preliminary Results – NH3 Base Run – January 2002, NC Monthly Average ppbv
Preliminary Results – NH3 Reduced Run – January 2002, NC Monthly Average
Preliminary Results – NH3 Difference Between Base Run and Reduced Run January 2002, NC - Monthly Average ppbv
Preliminary Results – NH3 Base Run – July 2002, NC Monthly Average ppbv
Preliminary Results – NH3 Reduced Run – July 2002, NC Monthly Average
Preliminary Results – NH3 Difference Between Base Run and Reduced Run July 2002, NC - Monthly Average ppbv
Preliminary Results PM2.5 Difference Between Base Run and Reduced Run January 2002, NC - Monthly Average
Preliminary Results PM2.5 Difference Between Base Run and Reduced Run July 2002, NC - Monthly Average
Preliminary Results–NH4+ Aerosol Base Run – January 2002, NC Monthly Average
Preliminary Results–NH4+ Aerosol Reduced Run – January 2002, NC Monthly Average
Preliminary Results–NH4+ Aerosol Difference Between Base Run and Reduced Run January 2002, NC - Monthly Average
Preliminary Results–NH4+ Aerosol Base Run – July 2002, NC Monthly Average
Preliminary Results–NH4+ Aerosol Reduced Run – July 2002, NC Monthly Average
Preliminary Results–NH4+ Aerosol Difference Between Base Run and Reduced Run July 2002, NC - Monthly Average