RIVM report xxxxxx xxx
RIVM report xxxxxx xxx
RIVM report xxxxxx xxx
Create successful ePaper yourself
Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.
page 26 of 142 <strong>RIVM</strong> <strong>report</strong> 773301 001 / NRP <strong>report</strong> 410200 051<br />
7DEOH &RPSDULVRQ RI &2 HPLVVLRQV IRU (XURSHDQ FRXQWULHV RI &25,1$,5 H[FO QDWXUH DQG<br />
('*$5E\FRXQWU\0WRQ\HDU<br />
Country<br />
CORINAIR<br />
(excl.<br />
nature)<br />
EDGAR<br />
2.0<br />
CORINAIR/<br />
EDGAR 2.0<br />
CORINAIR/<br />
EDGAR 2.0,<br />
excl. biofuels<br />
CORINAIR/EDGAR 2.0,<br />
excl. biofuels and nonenery<br />
use and chemical<br />
feedstocks<br />
7RWDO <br />
Austria 53 78 0.7 0.8 0.9<br />
Belgium 103 121 0.9 0.9 0.9<br />
Bulgaria 91 76 1.2 1.2 1.2<br />
former Czechoslovakia 206 226 0.9 0.9 0.9<br />
Denmark 55 64 0.9 1.1 1.1<br />
Finland 55 88 0.6 1.0 1.1<br />
France 373 429 0.9 0.9 1.1<br />
Germany (former DDR) 303 305 1.0 1.0 1.0<br />
Germany (former BRD) 708 754 0.9 1.0 1.0<br />
Greece 74 79 0.9 1.0 1.0<br />
Hungary 60 75 0.8 0.8 0.9<br />
Ireland 32 37 0.9 0.9 0.9<br />
Italy 441 456 1.0 1.0 1.1<br />
Luxembourg 11 10 1.1 1.1 1.1<br />
Netherlands 159 177 0.9 0.9 1.1<br />
Norway 34 42 0.8 1.0 1.2<br />
Poland 402 386 1.0 1.1 1.1<br />
Portugal 47 52 0.9 1.0 1.1<br />
Romania 171 171 1.0 1.0 1.0<br />
Spain 279 236 1.2 1.2 1.3<br />
Sweden 86 110 0.8 1.4 1.6<br />
Switzerland 47 48 1.0 1.1 1.1<br />
United Kingdom 580 596 1.0 1.0 1.0<br />
In Table 1.6 differences larger than 10% have been underlined. As can be concluded the unmodified<br />
emission estimates sometimes vary considerably between EDGAR and CORINAIR. A correction for<br />
biofuel use (which is usually but not always excluded in the CORINAIR inventories) leads to more<br />
consistent results: the European totals deviate less than 5%. Still differences remain for several<br />
countries that might be partly caused by different CO 2 emission factors for non-energy use and use as<br />
feed stock of fossil fuels. In order to verify this CO 2 emission due to non-energy uses of fuels have<br />
been excluded from the EDGAR results and the result is listed in sixth column. Although for some<br />
countries this leads to an improvement, overall consistency is less with the exclusion of non-energy<br />
uses. As in CORINAIR methodologies and sector coverage with respect to biofuels and non-energy<br />
uses vary between countries, incidental differences with consistent inventories like EDGAR are<br />
likely. Overall, results are in reasonable to good agreement with each other and no major<br />
inconsistencies in the underlying energy data seem to exist.<br />
&RPSDULVRQRIRWKHUFRPSRXQGV<br />
The second validation step comprises a more detailed comparison of the CORINAIR and EDGAR<br />
results for CH 4 , CO, CO 2 ,N 2 O, NMVOC, NO x and SO 2 . In this comparison the link between the<br />
sectors is analogous to Table 1.4. Basically this comparison has been made by sector and by country<br />
and aggregated results are listed in Table 1.7. Here results are aggregated for three regions being<br />
Western and Eastern Europe separately and Europe as a whole. There are several different sub-totals<br />
given in the tables. In the second column is indicated which CORINAIR SNAP1 sectors are included<br />
in the sub-totals. These sub-totals are listed because in some cases the apportioning of emissions to<br />
SNAP sectors is not always consistent in CORINAIR. This applies for example to small differences<br />
in what a country considers SNAP01 ‘Public Power, cogeneration and district heating’, SNAP02