-
Change (%) in lead emissions 1990-2007 (EEA member countries)
-
Change in lead emissions
Located in
Data and maps
›
Maps and graphs
-
Sector split of emissions of selected heavy metals (EEA member countries)
-
Sector split of HM
Located in
Data and maps
›
Maps and graphs
-
Change (%) in PAH emissions 1990-2007 (EEA member countries)
-
Change in polycyclic aromatic hydrocarbons
Located in
Data and maps
›
Maps and graphs
-
Sector share of PAH emissions (EEA member countries)
-
Sector share of polycyclic aromatic hydrocarbons
Located in
Data and maps
›
Maps and graphs
-
Contribution to total change in ammonia emissions for each sector (EEA member countries)
-
Chart showing sector contribution in the total percentage change of NH3 emissions between 1990 and 2007.
Located in
Data and maps
›
Maps and graphs
-
Contribution to total change in non-methane volatile organic compounds emissions for each sector (EEA member countries)
-
Chart showing sector contribution in the total percentage change of NMVOC emissions between 1990 and 2007.
Located in
Data and maps
›
Maps and graphs
-
Change in non-methane volatile organic compounds emissions for each sector between 1990 and 2007 (EEA member countries)
-
Chart showing percentage change of NMVOC emissions between 1990 and 2007, detail is shown by sectors.
Located in
Data and maps
›
Maps and graphs
-
Emission trends of nitrogen oxides (EEA member countries, EU-27 Member States)
-
The 'with measures' (WM) projections reported by Member States take into account currently implemented and adopted policies and measures. Where countries have instead reported 'business as usual' or 'current legislation' projections, it is assumed for comparison purposes that these are equivalent to a WM projection. The 'with additional measures' projections reported by Member States take into account additional future planned policies and measures but which are not yet implemented.
Located in
Data and maps
›
Maps and graphs
-
EEA-32 Nitrogen oxides (NOx) emissions (APE 002) - Assessment published Feb 2010
-
EEA-32 emissions of nitrogen oxides (NO x ) have decreased by 31% between 1990 and 2007. In 2007, the most significant sources of NO x emissions were the road transport sector (36%), combustion processes from within the energy industries sector (21%) and industrial energy use (15%) and the non-road transport sector (16%). The largest reduction of emissions since 1990 has occurred in the road transport sector. These reductions have been achieved despite the general increase in activity within this sector since the early 1990s and have primarily been achieved as a result of fitting three-way catalysts to petrol fuelled vehicles. In the electricity/energy production sector reductions have also occurred, in these instances as a result of measures such as the introduction of combustion modification technologies (such as use of low NO x burners), implementation of flue-gas abatement techniques (e.g. NO x scrubbers and selective (SCR) and selective non-catalytic (SNCR) reduction techniques) and fuel-switching from coal to gas. The National Emission Ceilings Directive (NECD) specifies NO x emission ceilings for Member States that must be met by 2010. In general, the newer Member States have made substantially better progress towards meeting their respective NOx ceilings than the older Member States of the EU-15. Eleven of the twelve post-2004 Member States have already reduced emissions beyond what is required under the NECD, or are very close to doing so (Bulgaria, Cyprus, the Czech Republic, Estonia, Hungary, Latvia, Lithuania, Poland, Romania, Slovakia and Slovenia). In contrast, only one EU-15 Member State (Portugal) has emissions within its respective national ceiling. Many Member States therefore must make significant cuts to NO x emissions in the immediate coming years if they are to meet their obligations under the NECD. Environmental context: NO x contributes to acid deposition and eutrophication. The subsequent impacts of acid deposition can be significant, including adverse effects on aquatic ecosystems in rivers and lakes and damage to forests, crops and other vegetation. Eutrophication can lead to severe reductions in water quality with subsequent impacts including decreased biodiversity, changes in species composition and dominance, and toxicity effects. It is NO 2 that is associated with adverse affects on human health, as at high concentrations it can cause inflammation of the airways. NO 2 also contributes to the formation of secondary particulate aerosols and tropospheric ozone in the atmosphere - both are important air pollutants due to their adverse impacts on human health.
Located in
Data and maps
›
Indicators
›
EEA-32 Nitrogen oxides (NOx) emissions
-
EEA-32 Sulphur dioxide SO2 emissions (APE 001) - Assessment published Feb 2010
-
EEA-32 emissions of sulphur dioxide (SO 2 ) have decreased by 69% between 1990 and 2007. In 2007, the most significant source of SO 2 emissions was the energy industries sector (69%), followed by emissions occurring from 'Other (Non Energy)' (20%) and industrial energy use (12%). The reduction in emissions since 1990 has been achieved as a result of a combination of measures, including fuel-switching in energy-related sectors away from high sulphur-containing solid and liquid fuels to low sulphur fuels such as natural gas, the fitting of flue gas desulphurisation abatement technology in industrial facilities and the impact of European Community directives relating to the sulphur content of certain liquid fuels. Seventeen of the EU-27 Member States have already reduced their national SO 2 emissions below the level of the emission ceilings set in the National Emission Ceilings Directive (NECD), while a number of others are close to meeting their ceilings. However, a small number of Member States still need to make significant further reductions in order to meet their respective ceilings under the NECD. Environmental context: Sulphur dioxide is emitted when fuels containing sulphur are combusted. It is a pollutant which contributes to acid deposition which in turn can lead to potential changes occurring in soil and water quality. The subsequent impacts of acid deposition can be significant, including adverse effects on aquatic ecosystems in rivers and lakes and damage to forests, crops and other vegetation. SO 2 emissions also contribute to formation of particulate matter in the atmosphere, an important air pollutant in terms of its adverse impact on human health.
Located in
Data and maps
›
Indicators
›
EEA-32 Sulphur dioxide SO2 emissions