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Daviz Visualization chemical/x-genbank Trend in winter oxidised nitrogen concentrations in coastal and open waters of the Baltic, Mediterranean Sea (Adriatic Sea) and North East Atlantic (Greater North Sea, Celtic Seas)
Located in Data and maps Data visualisations
Daviz Visualization Trend in winter orthophosphate concentrations in coastal and open waters of the Baltic, Mediterranean Sea (Western Mediterranean Sea, Adriatic Sea) and North East Atlantic (Greater North Sea, Celtic Seas, Bay of Biscay)
Located in Data and maps Data visualisations
Daviz Visualization C source code Trend in winter dissolved inorganic nitrogen concentrations in coastal and open waters of the Baltic, Mediterranean Sea (Adriatic Sea) and North East Atlantic (Greater North Sea)
Located in Data and maps Data visualisations
Figure Inland bathing water quality in the European Union, 1990-2012
The figure shows the bathing water quality in different European countries over time: 1990, 7 EU Member States; 1991 to 1994, 12 EU Member States; 1995-96, 14 EU Member States; 1997 to 2003, 15 EU Member States; 2004, 21 EU Member States; 2005-06, 25 EU Member States; 2007 to 2012, 27 EU Member States. No inland bathing waters are reported from three Member States (Cyprus, Malta and Romania). The quality classes under the New Bathing Water Directive (2006/7/EC) are jointed with compliance categories under the Bathing Water Directive (76/160/EEC).
Located in Data and maps Maps and graphs
Indicator Assessment Exposure of ecosystems to acidification, eutrophication and ozone (CSI 005) - Assessment published Dec 2013
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 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. Compared to 2009, the ozone indicators show a mixed behavior  Averaged over all rural background stations, the concentration relevant for the exposure of crops is slightly higher. However, the agricultural area exposed to concentrations above the target value did not increase in 2009 and 2010 compared to previous years, but the area exposed to levels between 12 000 and 18 000 (µg/m 3 ).hour is larger than in the previous years. With respect to the exposure of forests, the concentrations are similar compared to previous years. The effect-related concentrations, addressing exposure of crops to ozone over several summer months, show large year-to-year variations. Over the period 1996-2010 there is a tendency to increased exposure until 2006; and a tendency to decreasing levels after 2006. However, due to the large year-to-year variations, this development has not proven to be statistically significant.
Located in Data and maps Indicators Exposure of ecosystems to acidification, eutrophication and ozone
Indicator Assessment Passenger transport demand (CSI 035/TERM 012) - Assessment published Dec 2013
Between 2010 and 2011, passenger transport demand in the EU-28 (without Croatia) increased by nearly 1 %, reaching a new all-time high, mainly attributed to a 10 % increase in aviation. Demand steadily increased between 1995 and 2009, but at a slower rate than GDP. The largest increases have been in air (66 %) and car (23 %) demand between 1995 and 2011. However, the economic recession led to a decline in 2009 and 2010 (0.1 %). The car dominates the land passenger transport share at 76 %, followed by air (9 %) bus and coach (8 %) and rail (6 %).  Croatia experienced a 16 % increase in land passenger transport over the period 2001 to 2011. Land passenger demand, for the non-EU EEA Member States, also showed high growth. In particular, Turkey and Iceland at 53 % and 21 % respectively, compared to 7 % for the EU-28. Regarding the modal split, Switzerland’s rail share has increased over the past decade, being around 18 % in 2011, by far the highest value within the EEA-33. Correspondingly, the share for car in Switzerland is below the EEA-33 average. Turkey has the highest modal share of bus and coach use within the EEA-33 although it declined from 60 % in 1995 to 44 % in 2011. Iceland and Norway have car shares well above the EEA-33 average at 89 % and 88 % respectively.
Located in Data and maps Indicators Passenger transport demand
Indicator Assessment Oxygen consuming substances in rivers (CSI 019) - Assessment DRAFT created Sep 2013
Concentrations of BOD and total ammonium have decreased in European rivers in the period 1992 to 2011 (Fig. 1), mainly due to general improvement in wastewater treatment. See also WISE interactive maps: Mean annual BOD in rivers and Mean annual Total Ammonium in rivers
Located in Data and maps Indicators Oxygen consuming substances in rivers
Figure BOD5 concentrations in rivers between 1992 and 2011 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 lakes (total phosphorus) between 1992 and 2011 in different geographical regions of Europe.
The data series per region are calculated as the average of the annual mean concentrations 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 Phosphorus concentrations in rivers (orthophosphate) between 1992 and 2011 in different sea regions of Europe
The sea region data series are calculated as the average of annual mean concentrations for 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
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