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Change in cadmium, mercury and lead emissions for each sector between 1990 and 2010 (EEA member countries)
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Percentage change in cadmium (Cd), mercury (Hg) and lead (Pb) emissions for each sector between 1990 and 2010.
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Change (%) in HCH emissions 1990-2010 (EEA member countries)
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The reported change in hexachlorocyclohexane (HCH) emissions for each country, 1990-2010.
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Contribution to total change in ammonia (NH3) emissions for each sector (EEA member countries)
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The contribution made by each sector to the total change in ammonia (NH3) emissions between 1990 and 2010.
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Emission trends of ammonia (EEA member countries, EU-27 Member States)
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The with measures (WM) projections reported by Member States take into account currently implemented and adopted policies and measures
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Sulphur dioxide SO2 emissions (APE 001) - Assessment published Dec 2011
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EEA-32 emissions of sulphur dioxide (SO 2 ) have decreased by 76% between 1990 and 2009. In 2009, the most significant sectoral source of SO X emissions was Energy production and distribution (70%), followed by emissions occurring from Energy use in industry (13%) and in the Commercial, institutional and households (9%) sector. 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 Union directives relating to the sulphur content of certain liquid fuels. All of the EU-27 Member States have already reduced their national SO X emissions below the level of the 2010 emission ceilings set in the National Emission Ceilings Directive (NECD). Emissions in 2009 for the three non-EU countries having emission ceilings set under the UNECE/CLRTAP Gothenburg protocol (Liechtenstein, Norway and Switzerland) were also below the level of the respective 2010 ceilings. 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 X emissions also contribute as a secondary particulate pollutant to formation of particulate matter in the atmosphere, an important air pollutant in terms of its adverse impact on human health.
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Sulphur dioxide SO2 emissions
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Ammonia (NH3) emissions (APE 003) - Assessment published Dec 2011
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EEA-32 emissions of NH 3 have declined by 26% between the years 1990 and 2009. Agriculture was responsible for 94% of NH 3 emissions in 2009.
The reduction in emissions within the agricultural sector is primarily due to a reduction in livestock numbers (especially cattle) since 1990, changes in the handling and management of organic manures and from the decreased use of nitrogenous fertilisers. The reductions achieved in the agricultural sector have been marginally offset by the increased emissions which have occurred during this period in transport sectors and to a lesser extent the ‘Solvent and product use’ sector.
In general, Member States have made excellent progress in reducing emissions below the level of their respective emission ceilings set in the National Emission Ceilings Directive (NECD). Preliminary data released by EEA in February 2011 show that 26 of the 27 EU Member States report that they have achieved their ceilings. Finland is the only Member State which has exceeded its 2010 ceiling.
Three non-EU countries have emission ceilings set under the UNECE/CLRTAP Gothenburg protocol (i.e. Liechtenstein, Norway and Switzerland). The preliminary data recently received from these countries indicates only Liechtenstein has not met its 2010 emission ceiling.
Environmental context: NH 3 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. NH 3 also contributes to the formation of secondary particulate aerosols, an important air pollutant due to its adverse impacts on human health.
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Ammonia (NH3) emissions
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Emission trends of acidifying pollutants (EEA member countries, EU-27)
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This chart shows past emission trends of nitrogen oxides (NOx), sulphur oxides (SOx) and ammonia (NH3) in the EEA-32 and EU-27 group of countries. In addition - for the EU-27 - the aggregated Member State 2010 emission ceilings for the respective pollutants are shown
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Sector contributions of emissions of primary particulate matter and secondary precursors (EEA member countries)
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The contribution made by different sectors to emissions of primary PM2.5 and PM10, and to emissions of the secondary particulate matter precursors.
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Emissions of primary particulate matter and secondary particulate matter precursors (CSI 003) - Assessment published Dec 2011
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Total emissions of primary PM 10 particulate matter have reduced by 27% across the EEA-32 region between 1990 and 2009, driven by a 34% reduction in emissions of the fine particulate matter (PM 2.5 ) fraction; emissions of particulates between 2.5 and 10 µm have risen slightly (10%) over the same period.
Of this reduction in PM 10 emissions, 37% has taken place in the 'Energy Production and Distribution' sector due reasons including the fuel-switching from coal to natural gas for electricity generation and improvements in the performance of pollution abatement equipment installed at industrial facilities.
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Emissions of primary particulate matter and secondary particulate matter precursors
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Non-methane volative organic compounds (NMVOC) distance-to-target for EEA member countries
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The distance-to-target indicator shows how current emissions compare to a linear emission reduction 'target-path' between 1990 emission levels and the 2010 emission ceiling for each country. Negative percentage values indicate the current emissions in a country are below the linear target path; positive values show that current emission lie above a linear target path to 2010.
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