Data services overview

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Organic farming in the EU has been continuously increasing since 2012 and extended over million hectares in 2020, representing 9.1% of the utilised agricultural area (UAA).

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The figure shows the spatial variation in nitrogen (N) surplus (left map) and phosporus (P) surplus (right map) for all agricultural land in the EU-27 in 2010 (excluding the United Kingdom and Croatia). The surplus for N is calculated as the sum of N inputs to land (fertiliser, manure and biosolids, atmospheric N deposition, biological fixation and net mineralisation) minus crop removal (offtake). The surplus for P is calculdated as the sum of P inputs to land (fertiliser, manure and biosolids, atmospheric P deposition) minus crop removal (offtake). In the two maps, regions with higher N and P surpluses are coloured in shades of orange and red (with red colours representing N surpluses over 150 kg/ha/yr and P surpluses of 12 kg/ha/yr, respectively). Regions with lower N and P surpluses are shown in shades of green. N surpluses occur in nearly all regions, and are highest in areas with high livestock densities such as the Netherlands, Belgium, Brittany in France and the Po valley region in Italy. Because P is adsorbed by the soil, P surpluses can be negative in areas where crop uptake exceeds P input and P inputs are completely eliminated (so-called P mining), such as in parts of France, Germany, Czechia, Slovakia and Hungary. The maps and the supporting information are adapted from De Vries, W., Romkens, P., Kros, H., Voogd, J.C.H., Schulte-Uebbing, L., 2022, Impacts of nutrients and heavy metals in European agriculture. Current and critical inputs in relation to air, soil and water quality, ETC-DI Report 2022/01, European Environment Agency.

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Wheat yield losses at country level, expressed in % of yield loss, aggregated from the regional NUTS2 level losses

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This data set show the European agriculture area in 2018 at 100m spatial resolution, covering EEA38 member countries and the United Kingdom. The raster value is 1 when agricultural area is identified and NoData for other land cover / land uses.

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The pan-European High-Resolution Vegetation Phenology and Productivity product suite (HR-VPP) are provided at a high spatial resolution (10 m x 10 m) with a high repeat frequency. They are derived from the optical Sentinel-2 constellation data (Sentinel-2A and Sentinel-2B) with a revisit time of 5 days. They are generated over the entire EEA39 region (33 member countries and 6 cooperating countries) from January 1 2017 onwards, with a daily, 10-daily and yearly frequency (see below). The HR-VPP product suite contains 3 product groups, 31 product types, 1522 files and more than 900.000 tiles per year, which totals more than 80 Terra Bytes of data, per year.

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Greenhouse gas emissions from the agriculture sector are covered by national annual emission targets. Between 2005 and 2019, the EU’s agriculture emissions remained stable. Current national projections only foresee a modest decline of 2% by 2030, compared with 2005 levels, and a 5% reduction with the implementation of currently planned measures. This projected progress remains largely insufficient and highlights the need for further action if Member States are to reach their binding annual targets and the EU its climate neutrality goal by 2050.

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Birds and butterflies are sensitive to environmental change and can indicate the health of the environment. Long-term monitoring shows significant declines in farmland birds and grassland butterflies. Between 1990 and 2019, the index of 168 common birds decreased by 8% in the 25 EU Member States with monitoring schemes. The decline in common farmland birds over the same period was much more pronounced at 27%, while the common forest bird index increased by 5%. Between 1991 and 2018 the grassland butterfly index also declined strongly, by 25%, in the 19 EU countries with monitoring data.

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Greenhouse gas emissions from the agriculture sector are covered by national annual emission targets. Between 2005 and 2019, the EU’s agriculture emissions remained stable. Current national projections only foresee a modest decline of 2% by 2030, compared with 2005 levels, and a 5% reduction with the implementation of currently planned measures. This projected progress remains largely insufficient and highlights the need for further action if Member States are to reach their binding annual targets and the EU its climate neutrality goal by 2050.

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Birds and butterflies are sensitive to environmental change and can indicate the health of the environment. Long-term monitoring shows significant declines in farmland birds and grassland butterflies. Between 1990 and 2019, the index of 168 common birds decreased by 8% in the 25 EU Member States with monitoring schemes. The decline in common farmland birds over the same period was much more pronounced at 27%, while the common forest bird index increased by 5%. Between 1991 and 2018 the grassland butterfly index also declined strongly, by 25%, in the 19 EU countries with monitoring data.

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The figure shows the spatial variation in nitrogen (N) surplus (left map) and phosporus (P) surplus (right map) for all agricultural land in the EU-27 in 2010 (excluding the United Kingdom and Croatia). The surplus for N is calculated as the sum of N inputs to land (fertiliser, manure and biosolids, atmospheric N deposition, biological fixation and net mineralisation) minus crop removal (offtake). The surplus for P is calculdated as the sum of P inputs to land (fertiliser, manure and biosolids, atmospheric P deposition) minus crop removal (offtake). In the two maps, regions with higher N and P surpluses are coloured in shades of orange and red (with red colours representing N surpluses over 150 kg/ha/yr and P surpluses of 12 kg/ha/yr, respectively). Regions with lower N and P surpluses are shown in shades of green. N surpluses occur in nearly all regions, and are highest in areas with high livestock densities such as the Netherlands, Belgium, Brittany in France and the Po valley region in Italy. Because P is adsorbed by the soil, P surpluses can be negative in areas where crop uptake exceeds P input and P inputs are completely eliminated (so-called P mining), such as in parts of France, Germany, Czechia, Slovakia and Hungary. The maps and the supporting information are adapted from De Vries, W., Romkens, P., Kros, H., Voogd, J.C.H., Schulte-Uebbing, L., 2022, Impacts of nutrients and heavy metals in European agriculture. Current and critical inputs in relation to air, soil and water quality, ETC-DI Report 2022/01, European Environment Agency.

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Wheat yield losses at country level, expressed in % of yield loss, aggregated from the regional NUTS2 level losses

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• Total water input is expressed in m3/ha and gross value added is expressed in purchasing power standard (PPS)/ha, where the area in ha represents the sum of arable land and land with permanent crops. The monetary unit being used (PPS) accounts for purchasing power differences among countries. Theoretically, one PPS can buy the same amount of goods and services in each country. • Water use intensity of crop production is classified at the regional level according to the quartile (Q) distribution of all time series (2005-2016): below Q1 (light blue) indicates a low water intensity of crop production; above Q3 (dark blue) indicates a high water intensity of crop production; and between Q1 and Q3 (mid-blue) indicates a moderate water intensity of crop production. • Regional groupings of EU Member States and the UK are based on UN Geoscheme — Standard M49: eastern Europe (Bulgaria, Czechia, Hungary, Poland, Romania and Slovakia), northern Europe (Denmark, Estonia, Finland, Ireland, Lithuania, Latvia, Sweden and the United Kingdom), southern Europe (Cyprus, Greece, Croatia, Italy, Malta, Portugal, Slovenia and Spain) and western Europe (Austria, Belgium, Germany, France, Luxembourg and the Netherlands). • Gap filling has been performed for certain years and countries: 2010 data have been used for 2011 Greece data; 2006 data have been used for 2007 Hungary data; 2005 data have been used for 2007 Luxembourg data; 2009 data have been used for 2010 Portugal data; 2015 data have been used for 2016 Sweden data.

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Organic farming in the EU has been continuously increasing since 2012 and extended over million hectares in 2020, representing 9.1% of the utilised agricultural area (UAA).

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The European Commission has developed a set of risk indicators on chemical pesticides to track progress towards the Zero Pollution and Farm to Fork target for pesticide reduction. These indicators show that the risk and use of pesticides has decreased by 14% since the baseline period in 2015-2017.

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