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Indicator Assessment Municipal waste generation (CSI 016/WST 001) - Assessment DRAFT created Jan 2013
One of the most important objectives of the EU policy is to decouple waste generation from economic growth. Data shows that Municipal Solid Waste (MSW) generation in the EU-27 has been stabilising since 2000 albeit a high level of around 520 kg/capita. The effect of the economic downturn at the end of 2008 can be a reason of the further reductions in the amount of municipal waste generation from 2008 to 2011.
Located in Data and maps Indicators Municipal waste generation
Indicator Assessment Emissions of primary PM2.5 and PM10 particulate matter (CSI 003/APE 009) - Assessment published Dec 2012
Total emissions of primary sub-10µm particulate matter (PM 10 ) have reduced by 26% across the EEA-32 region between 1990 and 2010, driven by a 28% reduction in emissions of the fine particulate matter (PM 2.5 ) fraction. Emissions of particulates between 2.5 and 10 µm have reduced by 21% over the same period; the difference of this trend to that of PM 2.5 is due to significantly increased emissions in the 2.5 to 10 µm fraction from 'Road transport' and 'Agriculture' (of 50% and 15% respectively) since 1990. Of this reduction in PM 10 emissions, 39% has taken place in the 'Energy Production and Distribution' sector due to factors 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.
Located in Data and maps Indicators Emissions of primary PM2.5 and PM10 particulate matter
Indicator Assessment Emissions of ozone precursors (CSI 002/APE 008) - Assessment published Dec 2012
Emissions of the main ground-level ozone precursor pollutants have decreased across the EEA-32 region between 1990 and 2010; nitrogen oxides (NO X ) by 42%, non-methane volatile organic compounds (NMVOC) by 53%, carbon monoxide (CO) by 61%, and methane (CH 4 ) by 32%. This decrease has been achieved mainly as a result of the introduction of catalytic converters for vehicles, which has significantly reduced emissions of NO X and CO from the road transport sector, the main source of ozone precursor emissions. The EU-27 as a whole has not met its 2010 target to reduce emissions of NO X , one of the two ozone precursors (NO X and NMVOC) for which emission limits exist under the EU's NEC Directive (NECD). Whilst total NMVOC emissions in the EU-27 were below the NECD limit in 2010, a number of individual Member States did not meet their ceilings for one or both of these two pollutants. Of the three non-EU countries having emission ceilings for 2010 set under the UNECE/CLRTAP Gothenburg protocol (Liechtenstein, Norway and Switzerland), all reported NMVOC emissions in 2010 that were lower than their respective ceilings, however Liechtenstein and Norway reported NO X emissions higher than their ceiling for 2010.
Located in Data and maps Indicators Emissions of ozone precursors
Indicator Assessment Emissions of acidifying substances (CSI 001/APE 007) - Assessment published Dec 2012
Emissions of the acidifying pollutants, nitrogen oxides (NO X ), sulphur oxides (SO X ) and ammonia (NH 3 ), have decreased significantly in most of the individual EEA member countries between 1990 and 2010. Emissions of SO X have decreased by 75%, NO X by 42% and NH 3 emissions by 28% since 1990 within the EEA-32. Data reported under the NECD indicates that the EU-27 as a whole has met its overall target to reduce emissions of SO X and NH 3 as specified by the EU’s National Emissions Ceiling Directive (NECD). However twelve individual Member States, and the EU as a whole, reported emissions in the 2010 above their NECD 2010 emission ceilings for NO X , although the twelve Member States joining the EU in 2004/7 reported combined emissions below their collective NECD ceiling. Three EU-27 member states also reported 2010 NH 3 emissions above the levels of their NECD ceilings, neither of which are in the group of twelve new EU member states. Of the three non-EU countries having emission ceilings for 2010 under the UNECE/CLRTAP Gothenburg protocol (Liechtenstein, Norway and Switzerland), both Liechtenstein and Norway reported NO X emissions in 2010 that were substantially higher than their respective 2010 ceilings. Liechtenstein also reported 2010 NH 3 emissions above the level of their Gothenburg protocol 2010 ceiling.
Located in Data and maps Indicators Emissions of acidifying substances
Indicator Assessment Production and consumption of ozone depleting substances (CSI 006) - Assessment published Dec 2012
The total production and consumption of ozone depleting substances in EEA member countries has decreased significantly since the Montreal Protocol was signed in 1987 -  nowadays it is practically zero. Globally, the implementation of the Montreal Protocol has led to a decrease in the atmospheric burden of ozone-depleting substances (ODSs) in the lower atmosphere and in the stratosphere. Many of the ODS are also potent greenhouse gases in their own right, but as they are governed through the Montreal Protocol, they are not separately regulated under the UN Framework Convention on Climate Change (UNFCCC). Thus the phasing out of ODS under the Montreal Protocol has also avoided global greenhouse gas emissions. In 2010, it has been estimated that the reduction of greenhouse gas emissions  achieved under the Montreal Protocol was 5 to 6 times larger than that which will result from the UNFCCC's Kyoto Protocol first commitment period, 2008-2012.
Located in Data and maps Indicators Production and consumption of ozone depleting substances
Figure Water scarcity and drought events in Europe during the last decade
The map shows the main drought events in Europe in 2002 - 2011
Located in Data and maps Maps and graphs
Figure BOD5 concentrations in rivers between 1992 and 2010 draining to different sea regions of Europe
The sea region data series are calculated as the average of annual mean data from river monitoring stations in each sea region. The data thus represents rivers or river basins draining into that particular sea. Only complete series after inter/extrapolation are included (see indicator specification). The number of river monitoring stations included per sea region is given in parentheses. There were no stations with consistent data series on BOD7 in rivers draining to the Arctic Ocean. BOD7 data has been recalculated into BOD5 data.
Located in Data and maps Maps and graphs
Figure Phosphorus concentrations in rivers (orthophosphate) between 1992 and 2010 in different sea regions of Europe
The sea region data series are calculated as the average of annual mean data from river monitoring stations in each sea region. The data thus represents rivers or river basins draining into that particular sea. Only complete series after inter/extrapolation are included (see indicator specification). The number of river monitoring stations per sea region is given in parentheses.
Located in Data and maps Maps and graphs
Figure Phosphorus concentrations in lakes (total phosphorus) between 1992 and 2010 in different geographical regions of Europe.
The data series per region are calculated as the average of the annual mean for river monitoring stations in the region. Only complete series after inter/extrapolation are included (see indicator specification). There were no stations with complete series after inter/extrapolation in the South and Southeast regions. The number of lake monitoring stations included per geographical region is given in parentheses
Located in Data and maps Maps and graphs
Figure object code Percentage of ecosystem area at risk of acidification for EEA Member Countries and EEA Cooperating Countries in 2010 for a current legislation (CLE) scenario
The results were computed using the 2008 Critical Loads database. Deposition data was made available by the LRTAP Convention EMEP Centre for Integrated Assessment Modelling (CIAM) at the International Institute for Applied Systems Analysis (IIASA) in autumn 2007.
Located in Data and maps Maps and graphs
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