Data centre overview

The map describes the number OPS facilities available in the EEA area. The graph describes the number of ports equipped with OPS facilities in the EU and the total number of OPS facilities available.

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This map reports the NOx emissions from ships in sea areas of the EU (calculated as NO2) during the year 2019

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The Water Framework Directive aims to achieve good status for all rivers, lakes and transitional and coastal waters in the EU. Achieving good ecological status for surface waters is critical to this. According to countries’ second river basin management plans, good ecological status had been achieved for around 40% of surface waters (rivers, lakes and transitional and coastal waters) by 2015. However, these plans show only limited improvement in ecological status since the first plans were published in 2009, with ecological status remaining similar for most water bodies.

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Ocean surface pH declined from 8.2 to below 8.1 over the industrial era as a result of an increase in atmospheric CO 2 concentrations. This decline corresponds to an increase in oceanic acidity of about 30%. Reductions in surface water pH are observed across the global ocean. Ocean acidification has impacts on marine organisms and has already affected the deep ocean, particularly at high latitudes. Models project further ocean acidification worldwide. The target under United Nations Sustainable Development Goal 14.3 is to minimise the impacts of this by 2030.

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This figure shows trends for the North-East Atlantic and the Baltic Sea in the status of assessed commercially exploited fish and shellfish stocks between 1947 and 2019. The shaded areas represent the confidence limits. For the Mediterranean and Black Seas, no GES threshold is available for reproductive capacity. The dashed horizontal line represents the 2003 level for these regions. Due to the reduced number of stocks available for the Eastern Mediterranean Sea (only two), the indicators are not shown for this region.

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The table shows the countries' reporting performance on the basis of Eionet Core Data Flows since 2005

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The EEA marine assessment grid is a vector dataset based on the 'EEA reference grid'. It covers the Seas and Marine areas surrounding Europe. Open sea areas are covered by 100 km polygon grid shapes. Coastal areas are covered by 20 km polygon grid shapes. The combined EEA assessment grid fills the entire area of interest with grid cells without gaps and overlaps. Data and assessment results spatially mapped to the EEA assessment grid ensures that data can be compared in a uniform way across the European regional seas.

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We all want to know the quality of 'our' local bathing area, beach or lake, and whether it conforms to EU standards. Below you will find a map viewer that will allow you to view on-line the quality of the bathing water in the more than 22 000 coastal beaches and freshwater bathing waters across Europe.

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The EU Bathing Waters Directive requires Member States to identify popular bathing places in fresh and coastal waters and monitor them for indicators of microbiological pollution (and other substances) throughout the bathing season which runs from May to September

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The map reflects the most recent available information at the EU-level on implementation of the Urban Waste Water Treatment Directive (UWWTD) in EU 28 plus Iceland based on data reported by the Member States (for reference year 2018) in 2020.

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Waste water treatment and reductions in nutrient losses from agriculture have led to significant improvements in water quality in Europe. However, many of Europe’s freshwater bodies are still not doing well and the condition of Europe’s seas is generally poor, partly because of pollution.

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Waste water treatment and reductions in nutrient losses from agriculture have led to significant improvements in water quality in Europe. However, many of Europe’s freshwater bodies are still not doing well and the condition of Europe’s seas is generally poor, partly because of pollution.

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The Water Framework Directive aims to achieve good status for all rivers, lakes and transitional and coastal waters in the EU. Achieving good ecological status for surface waters is critical to this. According to countries’ second river basin management plans, good ecological status had been achieved for around 40% of surface waters (rivers, lakes and transitional and coastal waters) by 2015. However, these plans show only limited improvement in ecological status since the first plans were published in 2009, with ecological status remaining similar for most water bodies.

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Ocean surface pH declined from 8.2 to below 8.1 over the industrial era as a result of an increase in atmospheric CO 2 concentrations. This decline corresponds to an increase in oceanic acidity of about 30%. Reductions in surface water pH are observed across the global ocean. Ocean acidification has impacts on marine organisms and has already affected the deep ocean, particularly at high latitudes. Models project further ocean acidification worldwide. The target under United Nations Sustainable Development Goal 14.3 is to minimise the impacts of this by 2030.

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As a main source of protein, commercial fish stocks and other commercial sea products are renewable resources, which could sustain human needs in the long term — if exploited in an appropriate manner. Although further improvements are still necessary, the analysis of long time series shows clear and important signs of improvement in the North-East Atlantic Ocean and Baltic Sea. At least 24-47 % of all stocks meet at least one of two criteria defining the Marine Strategy Framework Directive's 'good environmental status' (GES) in the regions respectively. Meeting these criteria means that the exploitation (i.e. fishing mortality, F) and reproductive capacity of the stocks are compatible with their maximum sustainable yield (MSY). While slightly less than half of all stocks in the region have adequate assessments allowing comparisons with at least one of the GES criteria (83% of these met at least one criterion), these assessed stocks account for approximately 75% of the landings in the NEA and Baltic Sea. Since the early 2000s, better management of fish and shellfish fisheries has contributed to a clear decrease in fishing pressure in these two regional seas, with the average fishing mortality close to F MSY  in 2018. This has led to signs of recovery in the reproductive capacity of several fish and shellfish stocks. If these efforts continue, fishing mortality in the region on average should remain near F MSY  and reproductive capacity should continue to improve towards the objective for healthy fish and shellfish stocks in the North-East Atlantic Ocean and Baltic Sea. In contrast, in the Mediterranean Sea and the Black Sea the situation remains critical.  Only six out of 70 stocks (8.6 %) in the Mediterranean Sea and none of the 7 stocks in the Black Sea meet at least one of the GES criteria in these regions. This is mainly due to the prevalence of overfishing and a significant lack of knowledge of the reproductive capacity state of fish and shellfish stocks. Most of the stocks considered in the Mediterranean Sea had adequate assessment to compare fishing mortality with the GES criterion, but few had measures or thresholds of reproductive capacity. In the Black Sea, five of the seven stocks had adequate assessments to evaluate fishing mortality but only one of these also had measures or thresholds for reproductive capacity. It is unlikely that the 2020 policy objective has been met in the Mediterranean and Black Seas. Given this context, the 2020 objective of having healthy commercial fish and shellfish populations is unlikely to have been met in Europe’s seas and further collective action is required.

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We all want to know the quality of 'our' local bathing area, beach or lake, and whether it conforms to EU standards. Below you will find a map viewer that will allow you to view on-line the quality of the bathing water in the more than 22 000 coastal beaches and freshwater bathing waters across Europe.

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The map reflects the most recent available information at the EU-level on implementation of the Urban Waste Water Treatment Directive (UWWTD) in EU 28 plus Iceland based on data reported by the Member States (for reference year 2018) in 2020.

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The WISE Water Framework Directive Quality Elements map contains information from the 2nd River Basin Management Plans (RBMPs) reported by EU Members States and Norway according to article 13 of the Water Framework Directive (WFD). The map shows the ecological status or potential of surface water bodies based on their quality elements status value. The following quality elements are presented: QE1 - Biological quality elements; QE1-1 - Phytoplankton; QE1-2 - Other aquatic flora QE1-2-1 - Macroalgae; QE1-2-2 - Angiosperms; QE1-2-3 - Macrophytes; QE1-2-4 - Phytobenthos; QE1-3 - Benthic invertebrates; QE1-4 - Fish; QE2 - Hydromorphological quality elements; QE2-1 - Hydrological or tidal regime; QE2-2 - River continuity conditions; QE2-3 - Morphological conditions; QE3 - Chemical and physico-chemical quality elements; QE3-1 - General parameters; QE3-1-1 - Transparency conditions; QE3-1-2 - Thermal conditions; QE3-1-3 - Oxygenation conditions; QE3-1-4 - Salinity conditions; QE3-1-5 - Acidification status; QE3-1-6 - Nutrient conditions; QE3-1-6-1 - Nitrogen conditions; QE3-1-6-2 - Phosphorus conditions and QE3-3 - River Basin Specific Pollutants.

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This map reports the NOx emissions from ships in sea areas of the EU (calculated as NO2) during the year 2019

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The map describes the number OPS facilities available in the EEA area. The graph describes the number of ports equipped with OPS facilities in the EU and the total number of OPS facilities available.

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The map describes the number LNG facilities available in the EEA area. The graph describes the number of ports equipped with LNG facilities in the EU and the total number of LNG facilities available.

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This figure shows trends for the North-East Atlantic and the Baltic Sea in the status of assessed commercially exploited fish and shellfish stocks between 1947 and 2019. The shaded areas represent the confidence limits. For the Mediterranean and Black Seas, no GES threshold is available for reproductive capacity. The dashed horizontal line represents the 2003 level for these regions. Due to the reduced number of stocks available for the Eastern Mediterranean Sea (only two), the indicators are not shown for this region.

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The table shows the countries' reporting performance on the basis of Eionet Core Data Flows since 2005

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The chart shows the scoring of countries’ reporting performance on the basis of Eionet Core Data Flows.

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