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Progress in the management of contaminated sites between 2006 and 2011, expressed per management step and against established targets where relevant
The NEC Directive covers four main air pollutants: sulphur dioxide (SO2), nitrogen oxides (NOx), non-methane volatile organic compounds (NMVOCs) and ammonia (NH3). These pollutants can cause respiratory problems, contribute to the acidification of soil and surface water, and damage vegetation.
The graph illustrates that energy systems differ in the extent and complexity of their impacts by presenting the projected life cycle land use of fossil, nuclear and renewable electricity systems in 2030. To understand the implications of increased bioenergy production, it is important to recognise that the land used for energy cropping is a natural resource, comprising soil, minerals, water and biota. Where bioenergy involves energy cropping it often necessitates changes to land use, with significant implications for related systems as well Other renewable technologies do also use some land and so do fossil and nuclear systems but the area is comparatively small. Nevetheless these technologies have other limitations.
(Environmental) Combined potential impacts of changes in summer and winter precipitation, heavy rainfall days, annual mean temperature, summer days, frost days, snow cover days and annual mean evaporation on soil erosion, soil organic carbon content, protected natural areas and forest fire sensitivity. (Economic) Combined potential impacts of changes in annual mean evaporation, summer days, snow cover days, frost days, changes in inundation heights of a 100 year river flood event and a sea level rise adjusted 100 year coastal storm surge event on agriculture, forestry, summer and winter tourism, energy supply and demand.
Standard precipitation Index for February 2012, for 1, 3, 6 and 12 months
Mapping of drought conditions in Europe as calculated by the CDI (based on SPI, soil moisture and fAPAR) for top left 21 March 2012, top right 21 May 2011, and bottom left 1 May 2003. 2003 was known as a dry year for large parts of Europe.
Calculations are based on wind velocity and soil texture. While the overall patterns of erosion are generally sound, the validation of erosion data can be challenging. The data presented are currently being validated through comparisons with national datasets and expert judgement. In this sense, zooming in on a specific locality can give the impression of a situation that differs from reality.
Calculated by the Revised Universal Soil Loss Equation (RUSLE). While the overall patterns of erosion are generally sound, the validation of erosion data can be challenging. The data presented are currently being validated through comparisons with national datasets and expert judgement. In this sense, zooming in on a specific locality can give the impression of a situation that differs from reality. In addition, the model used in this exercise does not consider localised intense precipitation.
SMOS provides a global image of surface soil moisture every three days; this map covers the period 8–15 June 2010. Yellow colours indicate drier soil surfaces; blue colours denote wetter conditions. SMOS can measure soil moisture levels to an accuracy of 4 % at a spatial resolution of 50 km — about the same as detecting a teaspoonful of water mixed into a handful of dry soil.
One of the major tasks undertaken in the framework of the Corine programme has been the establishment of a computerised inventory on land cover
The diagram shows the proportion of cities per country that falls in a particular class regarding the degree of average soil sealing.
The map shows the average soil sealing degree inside the UMZ of European core cities (core city defined in Urban Atlas / Urban Audit). Soil sealing degrees are represented in coloured dots. The city dots are overlaid onto a modelled map displaying the change in annual number of days with heavy rainfall between the reference periods 1961-1990 and 2071-2100.
The map shows soil sealing degree ranging from 0 - 100% in aggregated spatial resolution (100 x 100 m).
The European Pollutant Release and Transfer Register (E-PRTR) is a web-based register established by Regulation (EC) No 166/2006 which implements the UNECE PRTR Protocol.
For references, please go to https://www.eea.europa.eu/data-and-maps/find/global or scan the QR code.
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