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| | {{CF-links}} | | {{CF-links}} |
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| − | Version 1: 20.12.2006<br>
| + | The [http://cf-pcmdi.llnl.gov/ CF conventions web site] contains a |
| | + | [http://cf-pcmdi.llnl.gov/documents/cf-standard-names/10/cf-standard-name-table.html List of accepted CF Standard Names, choose ''Atmospheric Chemistry'' as a Category.] |
| | + | |
| | + | The list of standard names for aerosol ad chemicals accepted by October 29 2008 can be found [[LIST OF CHEMICAL SPECIES AND AEROSOLS|here]]. |
| | | | |
| | This table gives a list of variables that have been accepted by the CF community | | This table gives a list of variables that have been accepted by the CF community |
| | [http://www.cgd.ucar.edu/mailman/listinfo/cf-metadata CF mailing list]. | | [http://www.cgd.ucar.edu/mailman/listinfo/cf-metadata CF mailing list]. |
| | | | |
| − | Goto the the list of
| + | New names can be submitted to this list and are discussed by the CF community on this mailing list. |
| − | [[CF Standard Names - Proposed names for TF HTAP|HTAP Proposed Atmospheric Chemistry and Aerosol Names]]
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| − | | |
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| − | These standard_names on this page are used within [http://aqm.jrc.it/HTAP/ model intercomparison] within the Task Force on Hemispheric Transport of Air Pollution [http://www.htap.org/ TF HTAP]. However, as the simulations already started before the names have been officially approved by CF, some minor changes will be necessary.
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| − | ----
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| − | TABLE VERSION 1
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| − | | |
| − | {|{{prettytable}}
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| − | |- style="background-color:#FF00FF;font-weight:bold"
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| − | | width="446,25" Height="12,75" | CF Standard_name
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| − | | width="75,75" | Canonical unit
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| − | | width="198,75" | Explanation
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| − | | |
| − | |-
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| − | | Height="12,75" |
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| − | |
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| − | |
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| − | | |
| − | |- style="background-color:#CCFFCC;font-weight:bold"
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| − | | Height="12,75" | dry deposition flux at the surface
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| − | |
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| − | |
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| − | | |
| − | |-
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| − | | Height="102" | surface_dry_deposition_mass_flux_of_all_nitrogen_oxides_expressed_as_nitrogen
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| − | | kg m-2 s-1
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| − | | NOy is the sum of all simulated oxidized nitrogen species, out of NO, NO2, HNO3, HNO4, NO3aerosol, NO3(radical), N2O5, PAN, other organic nitrates. Dry deposition includes gravitational settling, impact scavenging, and turbulent deposition"
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| − | | |
| − | |-
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| − | | Height="12,75" |
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| − | |
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| − | |
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| − | | |
| − | |- style="background-color:#CCFFCC;font-weight:bold"
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| − | | Height="12,75" | stomatal flux
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| − | |
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| − | |
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| − | | |
| − | |-
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| − | | Height="63,75" | surface_wet_deposition_mass_flux_of_all_nitrogen_oxides_expressed_as_nitrogen
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| − | | kg m-2 s-1
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| − | | NOy is the sum of all simulated oxidized nitrogen species, out of NO, NO2, HNO3, HNO4, NO3aerosol, NO3(radical), N2O5, PAN, other organic nitrates
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| − | | |
| − | |-
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| − | | Height="12,75" |
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| − | |
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| − | |
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| − | | |
| − | |- style="background-color:#CCFFCC;font-weight:bold"
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| − | | Height="12,75" | emission fluxes
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| − | |
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| − | |
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| − | | |
| − | |-
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| − | | Height="12,75" | atmosphere_emission_mass_flux_of_nox_expressed_as_nitrogen
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| − | | kg m-2 s-1
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| − | | NOx=NO+NO2
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| − | | |
| − | | |
| − | |-
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| − | | Height="12,75" |
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| − | |
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| − | |
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| − | | |
| − | |- style="background-color:#CCFFCC"
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| − | |style="font-weight:bold" Height="12,75" | volume mixing ratios
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| − | |style="font-weight:bold" |
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| − | |
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| − | | |
| − | |-
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| − | | Height="12,75" | mole_fraction_of_ozone_in_air
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| − | | 1=mole mole-1
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| − | |
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| − | | |
| − | |-
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| − | | Height="12,75" | mole_fraction_of_cabon_monoxide_in_air
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| − | | 1=mole mole-1
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| − | |
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| − | | |
| − | |-
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| − | | Height="12,75" | mole_fraction_of_nitrogen_monoxide_in_air
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| − | | 1=mole mole-1
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| − | |
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| − | | |
| − | |-
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| − | | Height="12,75" | mole_fraction_of_nitrogen_dioxide_in_air
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| − | | 1=mole mole-1
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| − | |
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| − | | |
| − | |-
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| − | | Height="12,75" | mole_fraction_of_nitrogen_acid_in_air
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| − | | 1=mole mole-1
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| − | |
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| − | | |
| − | |-
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| − | | Height="12,75" | mole_fraction_of_peroxyacetyl_nitrate_in_air
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| − | | 1=mole mole-1
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| − | |
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| − | | |
| − | |-
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| − | | Height="12,75" | mole_fraction_of_hydroxyl_radical_in_air
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| − | | 1=mole mole-1
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| − | |
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| − | | |
| − | |-
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| − | | Height="12,75" | mole_fraction_of_sulfur_dioxide_in_air
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| − | | 1=mole mole-1
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| − | |
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| − | | |
| − | |-
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| − | | Height="12,75" | mole_fraction_of_hexachlorbiphenyl_in_air
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| − | | 1=mole mole-1
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| − | |
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| − | | |
| − | |-
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| − | | Height="12,75" | mole_fraction_of_alpha_hexachlorocyclohexane_in_air
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| − | | 1=mole mole-1
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| − | |
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| − | | |
| − | |-
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| − | | Height="12,75" | mole_fraction_of_mercury_in_air
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| − | | 1=mole mole-1
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| − | |
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| − | | |
| − | |-
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| − | | Height="12,75" | mole_fraction_of_divalent_mercury_in_air
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| − | | 1=mole mole-1
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| − | |
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| − | | |
| − | |-
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| − | | Height="12,75" | mole_fraction_of_anthropogenic_non_methane_volatile_organic_compounds_in_air
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| − | | 1=mole mole-1
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| − | |
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| − | | |
| − | |-
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| − | | Height="12,75" | mole_fraction_of_biogenic_non_methane_volatile_organic_compounds_in_air
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| − | | 1=mole mole-1
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| − | |
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| − |
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| − | | |
| − | |-
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| − | | Height="12,75" |
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| − | |
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| − | |
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| − | | |
| − | |- style="background-color:#CCFFCC"
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| − | |style="font-weight:bold" Height="12,75" | mass mixing ratio
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| − | |style="font-weight:bold" |
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| − | |
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| − | | |
| − | |-
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| − | | Height="12,75" | mass_fraction_of_pm10_aerosol_in_air
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| − | | 1=kg kg-1
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| − | | The relative humidity should be given as as scalar coordinate variables using the standard name relative_humidity
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| − | | |
| − | |-
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| − | | Height="12,75" | mass_fraction_of_pm2p5_aerosol_in_air
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| − | | 1=kg kg-1
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| − | | The relative humidity should be given as as scalar coordinate variables using the standard name relative_humidity
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| − | | |
| − | |-
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| − | | Height="12,75" | mass_fraction_of_pm1_aerosol_in_air
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| − | | 1=kg kg-1
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| − | | The relative humidity should be given as as scalar coordinate variables using the standard name relative_humidity
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| − | | |
| − | | |
| − | |-
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| − | | Height="12,75" |
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| − | |
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| − | |
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| − | | |
| − | |- style="background-color:#CCFFCC"
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| − | |style="font-weight:bold" Height="12,75" | fluxes due to chemical reactions
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| − | |style="font-weight:bold" |
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| − | |
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| − | | |
| − | |-
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| − | | Height="12,75" | chemical_gross_production_rate_of_mole_concentration_of_ozone
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| − | | mole m-3 s-1
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| − | |
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| − | | |
| − | |-
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| − | | Height="12,75" | chemical_destruction_rate_of_mole_concentration_of_ozone
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| − | | mole m-3 s-1
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| − | |
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| − | | |
| − | |-
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| − | | Height="12,75" | chemical_destruction_rate_of_mole_concentration_of_methane
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| − | | mole m-3 s-1
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| − | |
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| − | | |
| − | |-
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| − | | Height="12,75" | chemical_destruction_rate_of_mole_concentration_of_carbon_monoxide
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| − | | mole m-3 s-1
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| − | |
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| − | | |
| − | |-
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| − | | Height="12,75" |
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| − | |
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| − | |
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| − | | |
| − | |- style="background-color:#CCFFCC"
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| − | |style="font-weight:bold" Height="12,75" | optical thickness
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| − | |
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| − | |
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| − | | |
| − | |-
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| − | | Height="38,25" | pm10_ambient_aerosol_optical_depth
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| − | | 1
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| − | | The wavelength should be given as as scalar coordinate variables using the standard name radiation_wavelength
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| − | | |
| − | |-
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| − | | Height="38,25" | pm2p5_ambient_aerosol_optical_depth
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| − | | 1
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| − | | The wavelength should be given as as scalar coordinate variables using the standard name radiation_wavelength
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| − | | |
| − | |-
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| − | | Height="38,25" | pm1_ambient_aerosol_optical_depth
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| − | | 1
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| − | | The wavelength should be given as as scalar coordinate variables using the standard name radiation_wavelength
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| − | | |
| − | |-
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| − | | Height="38,25" | nitrate_ambient_aerosol_optical_depth
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| − | | 1
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| − | | The wavelength should be given as as scalar coordinate variables using the standard name radiation_wavelength
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| − | | |
| − | |-
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| − | | Height="38,25" | sulfate_ambient_aerosol_optical_depth
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| − | | 1
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| − | | The wavelength should be given as as scalar coordinate variables using the standard name radiation_wavelength
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| − | | |
| − | |-
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| − | | Height="38,25" | ammonium_ambient_aerosol_optical_depth
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| − | | 1
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| − | | The wavelength should be given as as scalar coordinate variables using the standard name radiation_wavelength
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| − | | |
| − | |-
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| − | | Height="38,25" | black_carbon_ambient_aerosol_optical_depth
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| − | | 1
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| − | | The wavelength should be given as as scalar coordinate variables using the standard name radiation_wavelength
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| − | | |
| − | |-
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| − | | Height="38,25" | organic_carbon_ambient_aerosol_optical_depth
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| − | | 1
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| − | | The wavelength should be given as as scalar coordinate variables using the standard name radiation_wavelength
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| − | | |
| − | |-
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| − | | Height="38,25" | seasalt_ambient_aerosol_optical_depth
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| − | | 1
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| − | | The wavelength should be given as as scalar coordinate variables using the standard name radiation_wavelength
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| − | | |
| − | |-
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| − | | Height="38,25" | dust_ambient_aerosol_optical_depth
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| − | | 1
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| − | | The wavelength should be given as as scalar coordinate variables using the standard name radiation_wavelength
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| − | | |
| − | |-
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| − | | Height="38,25" | water_in_ambient_aerosol_optical_depth
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| − | | 1
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| − | | The wavelength should be given as as scalar coordinate variables using the standard name radiation_wavelength
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| − | | |
| − | |-
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| − | | Height="12,75" |
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| − | |
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| − | |
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| | | | |
| − | |}
| + | [[category:Climate Forecast Conventions]] |
