Benchmarking of chemical mechanisms

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Presentation transcript:

Benchmarking of chemical mechanisms Jean-François Lamarque, Peter Hess and Philip Cameron-Smith CCSM meeting, June 18, 2008

Rationale for benchmarking Three main chemical mechanisms (list of reactions and rates) are available: full, intermediate and fast. They differ in their decreasing representation of hydrocarbon chemistry and therefore their decreasing computational cost Gas-phase tropospheric chemistry only Full mechanism: 79 species Intermediate mechanism: 39 species Fast mechanism: 28 species

Purpose of interactive chemistry Provides distribution of radiatively-active greenhouse gases (troposphere and stratosphere) Provides distribution of oxidants for aerosol production (both online and offline) Provides distribution of secondary-organic aerosols Provides distribution of air quality Provides interaction with biogeochemistry: nitrogen deposition, ozone damage

Approach for benchmarking Simulation with relevance to air quality Simulation with relevance to climate High-resolution simulation (0.47°x0.63°) Driven by observed meteorology Compared with MIRAGE campaign observations (Mexico City pollution) Medium-resolution simulation (1.9°x2.5°) Driven by observed meteorology Two sets of emissions: base case and perturbed (30% reduction of Southeast Asia industrial sector, based on CCSP simulations) to study the response to a change in emissions Use full mechanism as “Truth”

Air quality: Comparison with Mexico City surface observations Day of Year (2006) Red: Full mechanism Green: Intermediate mechanism Blue: Fast mechanism Dots: observations On most days, full and intermediate capture well the diurnal cycle and amplitude; the fast mechanism is much lower

Air quality: Comparison with aircraft observations Day of Year (2006) Red: Full mechanism Green: Intermediate mechanism Blue: Fast mechanism Dots: observations On most days, full and intermediate capture well the background and plume ozone; the fast mechanism captures well the background. CO is will captured by all.

Climate: base emissions 300 hPa 500 hPa Surface January July Ozone mixing ratio Very good agreement amongst methods in radiatively important upper-troposphere ozone (but fixed stratosphere!); larger bias for the fast mechanism at lower altitudes Red: Full mechanism Green: Intermediate mechanism Blue: Fast mechanism

Climate: change in emissions Sulfate: important for indirect effect Nitric acid: important for nitrogen deposition OH: important for methane lifetime January July Change in surface mixing ratio Red: Full mechanism Green: Intermediate mechanism Blue: Fast mechanism Response in surface ozone and sulfate well captured; stronger biases for the fast mechanism for HNO3 and OH

Climate: change in emissions Change in 500 hPa mixing ratio Red: Full mechanism Green: Intermediate mechanism Blue: Fast mechanism

Climate: change in emissions Change in 250 hPa mixing ratio Red: Full mechanism Green: Intermediate mechanism Blue: Fast mechanism

Conclusions Background ozone is well represented by all chemical mechanisms Response in ozone and sulfate to changes in emissions is similar in all three mechanisms For the diagnostics selected, the intermediate mechanism is closer to the full mechanism and to observations than the fast mechanism, especially in strongly polluted regions Computational cost: Full = 5x CAM (3 tracers) Intermediate = 1/2 of full Fast = 1/3 of full, and could be reduced further for troposphere-only applications)