It has been acknowledged, that providing improved uncertainty
estimates is an urgent need for models and policy applications, but
also that it is hard to achieve on the short term other than
through collective expert judgement. Within the IPCC Inventory
Programme a special activity has recently been started aiming at
providing default values and a better framework for estimating and
reporting of uncertainties. A similar activity has started within
GEIA, aiming at the same results at country level as well as on
grid level, but for a more extended group of compounds and in a
more scientific setting. Comparisons of different datasets, e.g. as
done with the EDGAR data, may be an important input to this
process.
Therefore, it was decided by the EDGAR team that it was at
present not feasible to go beyond the uncertainty tables compiled
for Version 2.0 (see Table 1 and 2). However, in addition some
apparent conclusions on uncertainty can be drawn from the
comparison of V2.0 with other datasets as part of the validation
and check for urgent adaptations. For more detailed info on
uncertainty in specific inventories we refer to the papers on N2O,
NH3 and CO (Bouwman et al. 1995, 1997; Olivier et al, 1999) and
conclusions on validation in Olivier et al. (2001b).
To illustrate the usefulness of the uncertainty indications
presented here, we translated for methane the qualifications into
the percentage ranges mentioned in the notes of these tables. Next,
we compared the results with the uncertainty estimates used by IPCC
Working Group I for the preparation of the Third Assessment Report
(Fig. 1). The overall picture is rather similar, which shows that
this simple approach and interpretation of uncertainty ranges is
still quite useful for application at global levels. Table 1. Indication of uncertainty estimate for greenhouse
gases. Source: Olivier et al., 1999a. | Main source | Sub-category | Activity data | Emission Factor | . | . | Total Emissions | . | . | | . | . | . | CO2 | CH4 | N2O | CO2 | CH4 | N2O | | Fossil fuel use | Fossil fuel combusion | S | S | M | M | S | M | M | | . | Fossil fuel production | S | M | M | - | M | M | - | | Biofuel | Biofuel combustion | L | S | M | L | L | L | L | | Industry/solvent use | Iron & steel production | S | - | S | - | - | S | - | | . | Non-ferro production | S | - | S | - | - | S | - | | . | Chemicals production | S | - | S | L | - | S | M | | . | Cement production | S | S | - | - | S | - | - | | . | Solvent use | M | - | - | - | - | - | - | | . | Miscellaneous | V | - | - | - | - | - | - | | Landuse/ waste treatment | Agriculture | S | - | L | L | - | L | L | | . | Animals (excreta; ruminants) | S | - | M | L | - | M | L | | . | Biomass burning | L | S | M | L | L | L | L | | . | Landfills | L | - | M | - | - | L | - | | . | Agricultural waste burning | L | - | L | L | - | L | L | | . | Uncontrolled waste burning | L | - | - | - | - | - | - | | Natural sources | Natural soils | M | - | L | L | - | L | L | | . | Grasslands | M | - | M | L | - | M | L | | . | Natural vegetation | M | - | M | - | - | M | - | | . | Oceans/wetlands | M | - | L | L | - | L | L | | . | Lightning | S | - | - | - | - | - | - | | . | . | . | CO2 | CH4 | N2O | CO2 | CH4 | N2O | | All sources | . | - | - | - | - | S | M | L |
Notes: Expert judgement of uncertainty ranges, which were
assigned with the following classification in terms of order of
magnitude of the uncertainty in mind: S = small (10%); M = medium
(50%); L = large (100%); V = very large (>100%).
"-" Indicates that the compound is not applicable for this source
or that emissions are negligible. Table 2. Indication of uncertainty estimate for ozone and
aerosol precursors. Source: Olivier et al., 1996b | Main source | Sub-category | Activity data | . | . | . | . | Total Emissions | . | . | . | | . | . | . | CO | NOx | SO2 | NMVOC | CO | NOx | SO2 | NMVOC | | Fossil fuel use | Fossil fuel combusion | S | M | M | S | M | M | M | S | M | | . | Fossil fuel production | S | - | - | - | M | - | - | - | M | | Biofuel | Biofuel combustion | L | M | M | M | M | L | L | L | L | | Industry/solvent use | Iron & steel production | S | M | M | M | L | M | M | M | L | | . | Non-ferro production | S | M | M | L | L | M | M | L | L | | . | Chemicals production | S | M | M | L | L | M | M | L | L | | . | Cement production | S | - | - | - | - | - | M | - | - | | . | Solvent use | M | - | - | - | M | - | - | - | M | | . | Miscellaneous | V | - | - | - | V | - | - | - | V | | Landuse/ waste treatment | Agriculture | S | - | - | - | - | - | - | - | - | | . | Animals (excreta; ruminants) | S | - | - | - | - | - | - | - | - | | . | Biomass burning | M | M | L | M | L | L | L | L | L | | . | Landfills | L | - | - | - | - | - | - | - | - | | . | Agricultural waste burning | L | L | L | L | L | L | L | L | L | | . | Uncontrolled waste burning | L | - | - | - | L | - | - | - | V | | Natural sources | Natural soils | M | - | L | - | - | - | L | - | - | | . | Grasslands | M | - | - | - | - | - | - | - | - | | . | Natural vegetation | M | M | - | - | L | M | - | - | L | | . | Oceans/wetlands | M | L | - | - | - | L | - | - | - | | . | Lightning | S | - | L | - | - | - | L | - | - | | . | . | . | CO | NOx | SO2 | NMVOC | CO | NOX | SO2 | NMVOC | | All sources | . | - | - | - | - | - | M | M | M | L |
Notes: Expert judgement of uncertainty ranges, which were
assigned with the following classification in terms of order of
magnitude of the uncertainty in mind: S = small (10%); M = medium
(50%); L = large (100%); V = very large (>100%).
"-" Indicates that the compound is not applicable for this source
or that emissions are negligible. Figure 1. Comparison of uncertainty estimates for major global
methane sources using the uncertainty estimates by the EDGAR
team. 
Figure 2. Comparison of uncertainty estimates for major global
methane sources using the compilation for the Third Assessment
Report of IPCC Working Group I.

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