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Land take (CSI 014) - Assessment DRAFT created Apr 2013
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Land take by the expansion of residential areas and construction sites is the main cause of the increase in the coverage of urban land at the European level. Agricultural zones and, to a lesser extent, forests and semi-natural and natural areas, are disappearing in favour of the development of artificial surfaces. This affects biodiversity since it decreases habitats, the living space of a number of species, and fragments the landscapes that support and connect them. The annual land take in European countries assessed by 2006 Corine land cover project (EEA39 except Greece) was 107 968 ha/year in 2000-2006. In 21 countries covered by both periods (1990-2000 and 2000-2006) the annual land take decreased by 9 % in the later period. The composition of land taken areas changed, too. More arable land and permanent crops and less pastures and mosaic farmland were taken by artificial development then in 1990-2000. Identified trends are expected to change little when next assessment for 2006-2012 becomes available in 2014.
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Land take
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Intensity of land take 2000 - 2006
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Based on Corine Land Cover 2006 and changes between 2000 and 2006, the map shows the land take distribution and intensity for development of urban and other artificial area
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Annual production of major commercial aquaculture in different environments in Europe (EU-15+EFTA and EU-7, EU 2 + others), 1990-2008
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The figure shows the annual production of major commercial aquaculture in different environments in Europe
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Annual aquaculture production of major aquaculture species groups in Europe (EU-15+EFTA and EU-7, EU 2 + others), 1990-2008
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The figure show the annual aquaculture production of major aquaculture species groups in Europe
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Annual aquaculture production by country in (EU-15 + EFTA and EU-7, EU 2 + others), 2001 and 2008
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The figure shows the annual aquaculture production by country for 2001 and 2008
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Exposure of ecosystems to acidification, eutrophication and ozone (CSI 005) - Assessment published Nov 2012
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Eutrophication The magnitude of the risk of ecosystem eutrophication and its geographical coverage has diminished only slightly over the years. The predictions for 2010 and 2020 indicate that the risk is still widespread over Europe. This is in conflict with the EU's long-term objective of not exceeding critical loads of airborne acidifying and eutrophying substances in sensitive ecosystem areas (National Emission Ceilings Directive, 6th Environmental Action Programme, Thematic Strategy on Air Pollution).
Acidification The situation has considerably improved and it is predicted to improve further. The interim environmental objective for 2010 (National Emission Ceilings Directive) will most likely not be met completely. However, the European ecosystem areas where the critical load will be exceeded is predicted to have declined by more than 80 % in 2010 with 1990 as a base year. By 2020, it is expected that the risk of ecosystem acidification will only be an issue at some hot spots, in particular at the border area between the Netherlands and Germany.
Ozone (O 3 ) Most vegetation and agricultural crops are exposed to ozone levels exceeding the long term objective given in the EU Air Quality Directive. A significant fraction is also exposed to levels above the 2010 target value defined in the Directive. Concentrations in 2009 were on the average lower than in 2008. The effect-related accumulated concentrations, addressing exposure of crops to ozone over several summer months, shows large year-to-year variations. Over the period 1996-2009 there is a tendency to increased exposure, although this development has not proven to be statistically significant.
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Exposure of ecosystems to acidification, eutrophication and ozone
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Exposure of ecosystems to acidification, eutrophication and ozone (CSI 005) - Assessment published May 2012
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Eutrophication The magnitude of the risk of
ecosystem eutrophication and its geographical coverage has diminished
only slightly over the years. The predictions for 2010 and 2020 indicate
that the risk is still widespread over Europe. This is in conflict with
the EU's long-term objective of not exceeding critical loads of
airborne acidifying and eutrophying substances in sensitive ecosystem
areas (National Emission Ceilings Directive, 6th Environmental Action
Programme, Thematic Strategy on Air Pollution).
Acidification The situation has considerably
improved and it is predicted to improve further. The interim
environmental objective for 2010 (National Emission Ceilings Directive)
will most likely not be met completely. However, the European ecosystem
areas where the critical load will be exceeded is predicted to have
declined by more than 80 % in 2010 with 1990 as a base year. By 2020, it
is expected that the risk of ecosystem acidification will only be an
issue at some hot spots, in particular at the border area between the
Netherlands and Germany.
Ozone (O 3 ) Most
vegetation and agricultural crops are exposed to ozone levels exceeding the
long-term objective given in the EU Air Quality Directive. A significant
fraction is also exposed to levels above the 2010 target value defined in the
Directive. Concentrations in 2008 were on the average higher than in 2007. The
effect-related accumulated concentrations, addressing exposure of crops to
ozone over several summer months, shows large year-to-year variations, there is
a non-significance tendency to increase.
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Exposure of ecosystems to acidification, eutrophication and ozone
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Emissions of acidifying substances (CSI 001) - Assessment published Dec 2011
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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 2009. Emissions of SO X have decreased by 76%, NO X by 41% and NH 3 emissions by 26% since 1990.
The EU-27 is on track to meet its overall target to reduce emissions of SO X and NH 3 as specified by the EU’s National Emissions Ceiling Directive (NECD). However a number of individual Member States, and the EU as a whole, anticipates missing their NECD 2010 emission ceilings for NO X .
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 2009 that were substantially higher than their respective 2010 ceilings.
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Emissions of acidifying substances
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Non-methane volatile organic compounds (NMVOC) emissions (APE 004) - Assessment published Dec 2011
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EEA-32 emissions of non-methane volatile organic compounds (NMVOCs) have decreased by 51% since 1990. In 2009, the most significant sources of NMVOC emissions were ‘Solvent and product use’ (36%) (comprising activities such as paint application, dry-cleaning and other use of solvents), followed by ‘Commercial, institutional and households’ (15%).
The decline in emissions since 1990 has primarily been due to reductions achieved in the road transport sector due to the introduction of vehicle catalytic converters and carbon canisters on petrol cars, for evaporative emission control driven by tighter vehicle emission standards, combined with limits on the maximum volatility of petrol that can be sold in EU Member States, as specified in fuel quality directives. The reductions in NMVOC emissions have been enhanced by the switching from petrol to diesel cars in some EU countries, and changes in the ‘Solvents and product use' sector (a result of the introduction of legislative measures limiting for example the use and emissions of solvents).
The EU-27 Member States have, in general, made good progress towards reducing emissions in line with their obligations under the National Emission Ceilings Directive (NECD). Twenty four Member States (Austria, Belgium, Bulgaria, Cyprus, Czech Republic, Estonia, Finland, France, Greece, Hungary, Ireland, Italy, Latvia, Lithuania, Luxembourg, Malta, the Netherlands, Poland, Portugal, Romania, Slovakia, Slovenia, Sweden and the United Kingdom) have already reduced their national NMVOC emissions below the level of the emission ceilings set in the NECD. However, two Member States (Denmark and Germany) reported 2009 emissions significantly above their respective emission ceilings and therefore require significant reductions to have been made in 2010 in order to comply with the 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 all well below their respective ceilings.
Environmental context: Non-methane volatile organic compounds (NMVOCs) are a collection of organic compounds that differ widely in their chemical composition but display similar behaviour in the atmosphere. NMVOCs are emitted into the atmosphere from a large number of sources including combustion activities, solvent use and production processes. NMVOCs contribute to the formation of ground level (tropospheric) ozone, and certain NMVOC species such as benzene and 1,3 butadiene are hazardous to human health. Quantifying the emissions of total NMVOCs provides an indicator of the emissions of the most hazardous NMVOCs.
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Non-methane volatile organic compounds (NMVOC) 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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