Emission inventory

Compilation

For each of the pollutants in the inventory emissions are typically estimated by multiplying the intensity of each relevant activity ('activity rate') in the geographical area and time span with a pollutant dependent proportionality constant ('emission factor').

Why: the source categories

To compile an emission inventory, all sources of the pollutants must be identified and quantified. Frequently used source categorisations are

• those defined by the Intergovernmental Panel on Climate Change (IPCC) in the Revised 1996 IPCC Guidelines for National Greenhouse Gas Inventories Archived 2008-03-31 at the Wayback Machine, IPCC Good practice guidance and uncertainty management in national greenhouse gas inventories, IPCC Good practice guidance for land use, land use change and forestry and more recently the 2006 IPCC Guidelines for National Greenhouse Gas Inventories
• those defined in the UNECE Convention on Long-Range Transboundary Air Pollution (LRTAP); recently the LRTAP Convention adopted a source categorisation that is largely consistent with those of IPCC, to replace the more technology oriented Standardized Nomenclature for Air Pollutants (SNAP) used until 2005.

Both source categorisations make a clear distinction between sources related to the combustion of (fossil) fuels and those that are not caused by combustion. In most cases the specific fuel combusted in the former is added to the source definition. Source categories include:

1. Energy
   1. Fuel combustion
      1. Stationary combustion
         1. Industrial combustion
         2. Residential heating
      2. Mobile combustion (transport)
   2. Fugitive emissions from (fossil) fuel use
2. Industrial Processes
3. Solvent and other product use
4. Agriculture
5. LULUCF (Land Use, Land Use Change and Forestry)
6. Waste

Many researchers and research projects use their own source classifications, sometimes based on either the IPCC or the SNAP source categories, but in most cases the source categories listed above will be included.

What: the pollutants

Emission inventories have been developed and still are being developed for two major groups of pollutants:

• Greenhouse gases:
  • Carbon dioxide (CO₂),
  • Methane (CH₄),
  • Nitrous oxide (N₂O) and
  • A number of fluorinated gaseous compounds (HFCs, PFCs, SF₆)
  • Other greenhouse gases, not included in the United Nations Framework Convention on Climate Change (UNFCCC)
• Air pollutants:
  • Acidifying pollutants: sulphur dioxide (SO₂), nitrogen oxides (NO_x, a combination of nitrogen monoxide, NO and nitrogen dioxide, NO₂) and ammonia (NH₃),
  • Photochemical smog precursors: again nitrogen oxides and non-methane volatile organic compounds (NMVOCs)
  • Particulates and particulate precursors
  • Toxic pollutants like heavy metals and persistent organic pollutants
  • Carbon monoxide (CO)

Where: geographical resolution

Typically national inventories provide data summed at the national territory only. In some cases additional information on major industrial stacks ('point sources') is available. Stacks are also called release points, because not all emissions come from stacks. Other industrial sources include fugitive emissions, which cannot be attributed to any single release point.

Some inventories are compiled from sub-national entities such as states and counties (in the U.S.), which can provide additional spatial resolution.

In scientific applications, where higher resolutions are needed, geographical information such as population densities, land use or other data can provide tools to disaggregate the national level emissions to the required resolution, matching the geographical resolution of the model.

When: temporal resolution

Similarly, national emission inventories provide total emissions in a specific year, based on national statistics. In some model applications higher temporal resolutions are needed, for instance when modelling air quality problems related to road transport. In such cases data on time dependent traffic intensities (rush hours, weekends and working days, summer and winter driving patterns, etc.) can be used to establish the required higher temporal resolution.

Inventories compiled from Continuous Emissions Monitors (CEMs) can provide hourly emissions data.

How: methodology to compile an emission inventory

The European Environment Agency updated in 2007 the third edition of the inventory guidebook. The guidebook is prepared by the UNECE/EMEP Task Force on Emission Inventories and Projections and provides a detailed guide to the atmospheric emissions inventory methodology. Especially for Road Transport the European Environment Agency finances COPERT 4, a software program to calculate emissions which will be included in official annual national inventories.

Quality

The quality of an emission inventory depends on its use. In policy applications, the inventory should comply with all what has been decided under the relevant convention. Both the UNFCCC and LRTAP conventions require an inventory to follow the quality criteria below (see):

A well constructed inventory should include enough documentation and other data to allow readers and users to understand the underlying assumptions and to assess its usability in an intended application.

Sources and further reading

• United Nations Framework Convention on Climate Change
• Intergovernmental Panel on Climate Change
• U.S. Environmental Protection Agency: Clearinghouse for Inventories and Emissions Factors
• U.S. Environmental Protection Agency: National Greenhouse Gas Emissions Data
• U.S. Environmental Protection Agency: Toxics Release Inventory Archived 2015-06-27 at the Wayback Machine
• European Environment Agency EMEP/CORINAIR Emission Inventory Guidebook 2009
• U.S. Toxic Air Emissions Map
• COPERT 4 - Computer Programme to Calculate Emissions from Road Transport
• Use of RFID Inventory Management