The European Union established an inventory of emissions from large combustion plants in 2004. The inventory was governed by the Directive on the limitation of emissions of certain pollutants into the air from large combustion plants (LCP Directive, 2001/80/EC) until 2015 year. As from 2016 reporting year, the reporting takes place according to the Industrial Emissions Directive (2010/75/EU, Article 72). Large Combustion Plants are those with a rated thermal input equal to or greater than 50 MW, irrespective of the type of fuel used. Power plants, steel works or district heating plants are examples of these type of plants.
Indexed SO2, NOx and dust emissions from electricity generation for 2004 to 2015
The three graphs show the progression of emission limits in EU industrial emission policy over time. The example chosen is that emission limits for SO2, NOx and dust from existing large coal fired power plants.
The EEA coastline dataset has been created for detailed analysis (e.g.:1/100000) for geographical Europe. The coastline is a hybrid product obtained from satellite imagery from two projects: EUHYDRO (Pan-European hydrographic and drainage database) and GSHHG (A Global Self-consistent, Hierarchical, High-resolution Geography Database), as well as some manual amendments to meet requirements from EU Nature Directives, Water Framework Directive and Marine Strategy Framework Directive. In 2015, several corrections were made in the Kalogeroi Islands and two other Greek little islets, as well as in the peninsula of Porkkala. In this revision from 2017, two big lagoons have been removed from Baltic region, because, according to HELCOM, are freshwater lagoons.
Dashboard (Tableau)
07 Dec 2018
How many policies and measures (PaMs) did the European Member States implement or plan to implement to reduce greenhouse gas emissions? What type of policies, affecting which sectors have been primarily reported? Were the European Union policies driving the development of national policies? The European Environment Agency's viewer explores PaMs reported by Member States under the EU Monitoring Mechanism Regulation.
EEA member states (EEA-33) and cooperating countries
Indicator Assessment
06 Dec 2018
The coverage of ecosystem classes under the EU 'Mapping and Assessment of Ecosystems and their Services' (MAES) framework was affected by change processes between 2006 and 2012, with urbanisation the most dominant process. Urban ecosystems showed the highest net increase both in the EU-28 and in the EEA-33 countries, predominantly at the expense of cropland and grassland.
A very slight increase in coverage was observed in forest and woodland, while agricultural ecosystems, both cropland and grassland, continued to decrease.
Vulnerable ecosystems such as heathland and sparsely vegetated land (dunes, beaches, sand plains, bare rocks and glaciers) continued to disappear between 2006 and 2012, although the loss of wetlands seems to have levelled off for the first time over the same period. It should be borne in mind, however, that approximately two thirds of European wetlands were lost before the 1990s and their area has subsequently continued to decrease.
Data Visualization
06 Dec 2018
Indicator Assessment
30 Nov 2018
Noise pollution is a major environmental health problem in Europe.
Road traffic is the most widespread source of environmental noise, with more than 100 million people affected by harmful levels in the EEA-33 member countries. Railways, air traffic and industry are also major sources of noise.
The European Union's Seventh Environment Action Programme (7th EAP) sets the objective that by 2020 noise pollution in the EU will have significantly decreased, moving closer to World Health Organization (WHO) recommended levels.
This figure shows, the status of the assessed European fish stocks in relation to Good Environmental Status per regional sea in 2015. Stocks for which adequate information is available to determine GES for F and/or SSB are included in this figure (i.e. total number of assessed stocks). A distinction is made between stocks (i) in GES, based on both fishing mortality and reproductive capacity, (ii) in GES, based on either fishing mortality or reproductive capacity, and (iii) not in GES, based on fishing mortality and/or reproductive capacity (see methodology for further information on how GES is determined). As assessments are carried out in a multi-annual cycle within the Mediterranean, number of stocks included in this Figure for the Mediterranean depends on the time period the Figure covers
GIS Map Application
10 Oct 2018
This interactive map gives a European overview of water stress conditions. The information presented may deviate from that available in the EEA member countries and cooperating countries, particularly for those countries where data availability is insufficient in the WISE SoE – Water quantity database (WISE 3).
Data on hydro-climatic variables was aggregated from a daily to a monthly scale. Water abstraction data was taken from WISE 3 (annual resolution at the national scale), although there are large gaps in the time series. Therefore, intensive gap filling was performed on water abstraction data and proxies were used to disaggregate the data from the national to the sub-basin scale.
Information on water use was mainly modelled on the UWWTP capacities, the E-PRTR database and the Eurostat Population change dataset (online data code [demo_gind]) among others. See the methodology chapter for further explanation of gap filling, and spatial and temporal disaggregation, and the data uncertainties chapter for current data availability.
This interactive map allows users to explore changes over time in water abstraction by source, water use by sector and water stress level at sub-basin or river basin scale. The WEI+ has been estimated as the quarterly average per river basin district, for the years 1990-2015, as defined in the European catchments and rivers network system (ECRINS). The ECRINS delineation of river basin districts differs slightly from that defined by Member States under the Water Framework Directive. The Ecrins delineation is used instead of WFD because it contains geo-spatial information on Europe’s hydrographical systems with full topological information enabling flow estimation between upstream and downstream basins, as well as integration of economic data collected at NUTS or country level.
In addition to using e WISE SoE – Water quantity database, a comprehensive manual data collection was performed by accessing all open sources (Eurostat, OECD, FAO) including national statistical offices of the countries. This was done because of the temporal and spatial gaps in the data on water abstraction. Moreover, a large part of the stream flow data from LISFLOOD has also been substantially updated by the Directorate-General Joint Research Centre. Similarly, a comprehensive update with climatic parameters has been performed by the EEA based on the E-OBS dataset. Therefore, the time series of the WEI+ presented in the current version might be slightly different for some basins compared with the previous version.
GIS Map Application
01 Aug 2018
Latest measurements from Europe's air quality monitoring network
