摘要

<jats:p>We use the adjoint of a global 3‐D chemical transport model (GEOS‐Chem) to optimize ammonia (NH<jats:sub>3</jats:sub>) emissions in the U.S., European Union, and China by inversion of 2005–2008 network data for <jats:inline-graphic xmlns:xlink="http://www.w3.org/1999/xlink" xlink:href="graphic/jgrd51294-math-0001.gif" xlink:title="urn:x-wiley:jgrd:media:jgrd51294:jgrd51294-math-0001" /> wet deposition fluxes. Optimized emissions are derived on a 2° × 2.5° grid for individual months and years. Error characterization in the optimization includes model errors in precipitation. Annual optimized emissions are 2.8 Tg NH<jats:sub>3</jats:sub>−N a<jats:sup>−1</jats:sup> for the contiguous U.S., 3.1 Tg NH<jats:sub>3</jats:sub>−N a<jats:sup>−1</jats:sup> for the European Union, and 8.4 Tg NH<jats:sub>3</jats:sub>−N a<jats:sup>−1</jats:sup> for China. Comparisons to previous inventories for the U.S. and European Union show consistency (∼±15%) in annual totals but some large spatial and seasonal differences. We develop a new global bottom‐up inventory of NH<jats:sub>3</jats:sub> emissions (Magnitude And Seasonality of Agricultural Emissions model for NH3 (MASAGE_NH3)) to interpret the results of the adjoint optimization. MASAGE_NH3 provides information on the magnitude and seasonality of NH<jats:sub>3</jats:sub> emissions from individual crop and livestock sources on a 0.5° × 0.5° grid. We find that U.S. emissions peak in the spring in the Midwest due to corn fertilization and in the summer elsewhere due to manure. The seasonality of European emissions is more homogeneous with a well‐defined maximum in spring associated with manure and mineral fertilizer application. There is some evidence for the effect of European regulations of NH<jats:sub>3</jats:sub> emissions, notably a large fall decrease in northern Europe. Emissions in China peak in summer because of the summertime application of fertilizer for double cropping.</jats:p>

  • 出版日期2014-4-16