Difference between revisions of "MEGAN v2.1 plus Guenther 2012 biogenic emissions"

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--[[User:Bmy|Bob Y.]] 13:19, 3 March 2015 (EST)
 
--[[User:Bmy|Bob Y.]] 13:19, 3 March 2015 (EST)
  
=== Discussion about 1-month benchmark v10-01h ===
+
=== Discussion following 1-month benchmark v10-01h ===
  
 
This emission scheme was validated in [[GEOS-Chem_v10-01_benchmark_history#v10-01h|GEOS-Chem v10-01h]]. The following discussion ensued.
 
This emission scheme was validated in [[GEOS-Chem_v10-01_benchmark_history#v10-01h|GEOS-Chem v10-01h]]. The following discussion ensued.

Revision as of 17:12, 27 March 2015

On this page we describe the MEGAN v2.1 plus Guenther et al 2012 biogenic emissions, which are used in GEOS-Chem v10-01 and newer versions. The MEGAN emissions are fed into GEOS-Chem via the HEMCO emissions component.

Overview

Description

Dylan Millet wrote:

GEOS-Chem emission routines for biogenic VOCs have been updated to MEGAN2.1 as described in Guenther et al., Geosci. Model Dev., 5, 1471–1492, 2012. (Article) The net result is a 11-12% decrease in the global flux for isoprene, and a 30% increase in the global flux for total monoterpenes. Biogenic alkene emissions are now computed using MEGAN instead of by scaling to isoprene, as was done previously. Biogenic emissions of acetaldehyde are now included. Annual emission totals at 2x2.5 resolution for the different compounds are within ~20% of the values in Table 6 of Guenther et al., within the expected uncertainty associated with differing meteorology, years, etc. Note that global emissions can also change by 10% or more when running at 2x2.5 versus 4x5 degree horizontal resolution (for both the updated and the standard emission routines).
One of the ‘under-the-hood’ changes is that there is now a single driver routine for calculating MEGAN emissions across all compounds (GET_MEGAN_EMISSIONS). Previously we had separate driver routines for each individual compound. GET_MEGAN_EMISSIONS is passed the compound name, looks up or computes the appropriate parameters, and returns the corresponding emissions. This should hopefully make it much easier to add new compounds in the future, since one just has to add the appropriate parameter values for that compound. There are parameters included for a number of compounds not presently in the standard chemistry scheme - for use in specialized simulations and/or future inclusion in standard fullchem. Another under-the-hood change is that the PCEEA/PECCA flag is no longer needed since we use this scheme exclusively now.
The new MEGAN implementation computes emissions for certain compounds based on pre-defined emission factor maps provided with the MEGAN source code. For other compounds emissions are computed in GEOS-Chem based on CLM4 plant functional type distributions combined with PFT-specific emission factors. This PFT approach can be used for all MEGAN compounds if desired (by adding in the corresponding emission factors for each PFT), which may be useful for applications using different vegetation maps or dynamically shifting vegetation.
The updated emissions lead to lower CO concentrations in the Northern Hemisphere during summer. A GEOS-Chem v9-01-03 4x5 run for 2006 gave CO mixing ratios averaged for P>800 hPa) that were lower by a few ppb over much of the Northern Hemisphere during ummer months. Maximum decreases of about 10ppb occur over certain source regions. Ox changes are small (< 2ppb for P > 800hPa) using the standard v9-1-3 (non-Caltech) chemistry scheme.

Please contact Dylan Millet with any further questions about these emissions.

--Bob Y. 16:05, 25 February 2015 (EST)

Documentation

  • Comparison between previous and updated BVOC emissions for standard tracers (year-2006):
  • Comparison between previous and updated BVOC emissions for standard tracers (nested NA, year-2011):
  • Updated emissions for all BVOCs, including non-standard tracers:
  • Monthly CO comparison for previous and updated MEGAN implementation (year-2006; 4x5 resolution):

--Dbm 14:18, 22 January 2013 (EST)

Data files

In GEOS-Chem v10-01 and newer versions, the MEGAN v2.1 plus Guenther (2012) biogenic emissions are read with the HEMCO emissions component. We have created new MEGAN data files (in COARDS-compliant netCDF format) for use with HEMCO. These new data files are contained in the HEMCO data directory tree. For detailed instructions on how to download these data files to your disk server, please see our Downloading the HEMCO data directories wiki post.

--Bob Y. 13:19, 3 March 2015 (EST)

Discussion following 1-month benchmark v10-01h

This emission scheme was validated in GEOS-Chem v10-01h. The following discussion ensued.

Dylan Millet wrote:

A few comments and questions below.
1. Acetone
Based on the benchmarking I did earlier biogenic acetone emissions should increase 6-7% globally & annually with the MEGAN update. But the emission ratio plot for ACET in the new benchmark shows a >2x increase everywhere. On the emission summary page, the "biogenic and natural' acetone sources look to have increased from 1.6 to 5.2. But if we look on the same page at the "acetone sources" the two simulations are very similar and the sum is consistent with a ~7% increase. In other words the large discrepancy in the emission ratio plot and in the "biogenic and natural sources" table for acetone just looks to be a correction to the way the diagnostics are being done. Is that right? Consistent with that, the concentration ratios are not very different.
2. Isoprene
I'd expect about a 10-12% isoprene decrease globally & annually for isoprene emissions. The new benchmark has a ~30% decrease. I'm not sure why that would be. It could just be the difference between a 1-month run and a full year, or interannual variability, I suppose, though the discrepancy seems large for that. Does the 10-01f benchmark we're comparing to use the (old) standard canopy treatment, or does it use the PCEEA parameterization? That was an option before, but we got rid of it with the MEGAN update (which only uses PCEEA). If we're switching canopy schemes that might explain the difference.
3. For propene I expect about a 50% increase globally. The change we see in the benchmark is larger (67%) but not dramatically.
4. Since we now have biogenic emissions of ALD2 we should add the appropriate biogenic benchmark diagnostics.

Melissa Sulprizio wrote:

1. Acetone
That is correct. Prior to this version, there was a bug in diag3.F in the conversion to atomsC/cm2/s that affected the biogenic acetone diagnostic (ND46). The error appears to have come in with the implementation of HEMCO. We corrected the unit conversion in this version and the biogenic acetone emissions are now more consistent with pre-HEMCO values.
2. Isoprene
The PECCA/PCEEA model was turned off in the old benchmarks, so that may explain the difference. From the HEMCO.log file for the previous benchmark (v10-01f_UCX), we have:
     Use MEGAN biogenic emissions (extension module)
      - Use PECCA model:  F
      - Use the following species:
         Isoprene   = ISOP           1
         Acetone    = ACET          26
         C3 Alkenes = PRPE          23
         Ethene     = C2H4          -1
      --> Isoprene scale factor is    1.00000000000000
      - MEGAN monoterpene option enabled:
         CO         = CO          31
         OC aorosol = OCPI          16
         Monoterp.  = MONX          -1
3. Propene
Could it be that the difference in meteorology fields is causing this difference? It looks like your benchmarks used GEOS-5 met fields for 2006. In v10-01h, we are using GEOS-FP met fields for July 2013.
4. Diagnostics
I have added ALD2 to the benchmark plotting routines. We were unable to make difference plots for this version since v10-01f_UCX didn’t include biogenic emissions of ALD2 so I have that update commented out for now, but we will include differences of ALD2 biogenic emissions in future benchmarks. For your reference, I have included a map of the ALD2 biogenic emissions from v10-01h below:
V10-01h ALD2 biogenic emissions.gif

Dylan Millet wrote:

Ok, that all seems reasonable. The only question left in my mind is the 30% isoprene decrease compared to 10% that I saw earlier. I've started a run testing the impact of switching canopy schemes to see if that accounts for it.
Based on my original implementation of the MEGAN update, changing the MEGAN algorithms and EFs gives a 10-11% reduction in global emissions. Changing the canopy scheme gives another 7-8% decrease. So the total expected decrease (18%) is still less than we see with the new benchmark (30%), but close enough that it could be due to 1 month versus 1 year, different met fields, interannual variability, etc. I vote for moving ahead and having a look at the 1-y benchmark.

--Melissa Sulprizio 13:12, 27 March 2015 (EDT)

CO2 direct effect on isoprene emissions

This update is slated for inclusion in GEOS-Chem v10-01 or later

Amos Tai developed code updates to include CO2 inhibition of isoprene emissions in MEGAN.

The reference for this work is:

Tai, A.P.K., L.J. Mickley, C.L. Heald, S. Wu, Effect of CO2 inhibition on biogenic isoprene emission: Implications for air quality under 2000-to-2050 changes in climate, vegetation, and land use, Geophys. Res. Let., 40, 3479-3483, 2013. [pdf]

--Melissa Sulprizio 15:45, 23 January 2014 (EST)

References

  1. Barkley, M., Description of MEGAN biogenic VOC emissions in GEOS-Chem, 2010. PDF
  2. Buermann, W., Wang, Y.J., Dong, J.R., Zhou, L.M., Zeng, X.B., Dickinson, R.E., Potter, C.S., and Myneni, R.B.: Analysis of a multiyear global vegetation leaf area index data set, J. Geophys. Res., 107, 4646, doi:10.1029/2001JD000975, 2002.
  3. Guenther, A., Baugh, B., Brasseur, G., Greenberg, J., Harley, P., Klinger, L., Serca, D., and Vierling, L.: Isoprene emission estimates and uncertainties for the Central African EXPRESSO study domain, J. Geophys. Res., 104, 30625-30639, 1999.
  4. Guenther, A., Karl, T., Harley, P., Wiedinmyer, C., Palmer, P.I., and Geron, C.: Estimates of global terrestrial isoprene emissions using MEGAN (Model of Emissions of Gases and Aerosols from Nature), Atmos. Chem. Phys., 6, 3181-3210, 2006.
  5. Guenther, A., and C. Wiedinmyer, User's guide to the Model of Emissions of Gases and Aerosols from Nature (MEGAN), Version 2.01, 2007.
  6. Guenther, A. B., Jiang, X., Heald, C. L., Sakulyanontvittaya, T., Duhl, T., Emmons, L. K., and Wang, X.: The Model of Emissions of Gases and Aerosols from Nature version 2.1 (MEGAN2.1): an extended and updated framework for modeling biogenic emissions, Geosci. Model Dev., 5, 1471-1492, doi:10.5194/gmd-5-1471-2012, 2012. Article
  7. Millet, D.B., Jacob, D.J., Boersma, K.F., Fu, T.M., Kurosu, T.P., Chance, K., Heald, C.L., and Guenther, A.: Spatial distribution of isoprene emissions from North America derived from formaldehyde column measurements by the OMI satellite sensor, J. Geophys. Res., 113, D02307, doi:10.1029/2007JD008950, 2008. PDF
  8. Mueller, J.-F., et al. Global isoprene emissions estimated using MEGAN, ECMWF analyses and a detailed canopy environment model, Atmos. Chem. Phys., 8, 1329-1341, 2008.
  9. Myneni, R. B., et al., Large seasonal swings in leaf area of Amazon rainforests, Proceedings of the National Academy of Sciences, 104(12), 4820{4823, doi:10.1073/pnas.0611338104, 2007.
  10. Palmer, P.I., Abbot, D.S., Fu, T.M., Jacob, D.J., Chance, K., Kurosu, T.P., Guenther, A., Wiedinmyer, C., Stanton, J.C., Pilling, M.J., Pressley, S.N., Lamb, B., and Sumner, A.L.: Quantifying the seasonal and interannual variability of North American isoprene emissions using satellite observations of the formaldehyde column, J. Geophys. Res., 111, D12315, doi:10.1029/2005JD006689, 2006. PDF
  11. Sakulyanontvittaya, T., T. Duhl, C. Wiedinmyer, D. Helmig, S. Matsunaga, M. Potosnak, J. Milford, and A. Guenther, Monoterpene and Sesquiterpene Emission Estimates for the United States, Environ. Sci. Technol., 42(5), 1623{1629, doi:10.1021/es702274e, 2008.

--Bob Y. 15:49, 25 February 2015 (EST)