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  • Modeling of the content of topsoil organic carbon (%) (ISO 10694) in croplands (0-25 cm), permanent grasslands (0-10 cm), vineyards (0-30 cm) and forests (0-20 cm). Based on soil analysis data collected between 2012-2014 (agriculture, vineyards) and 1998-2001 (forest). Data not transformed into INSPIRE data model

  • Interpolation (Kriging) of the pH content (CaCl2) in agricultural soils. Based on soil analysis data from 2009 to 2014. Data not transformed into INSPIRE data model

  • This dataset contains the Soil map of the Grand-Duchy of Luxembourg at scale of 1:100.000. It contains a classification of the complete territory in 29 soil mapping units (SMU) containing information on texture, stoniness, nature of coarse fragments, drainage and simplified pedogenetic classification. The dataset has been published in 1969.

  • The flood risk management directive (directive 2007/60/CE) consider the development of flood risk management plans as an appropriate tool to prevent or reduce the adverse effects of flood events. The focus is particularly on prevention, protection and precautions. The catalog of measures drawn up for Luxembourg corresponds in its structure and basic statements to the German LAWA catalog of measures.

  • According to the water framework directive WFD(DIR 2000/60/CE), important physico chemical parameters are measured in the surface water bodies for the assessment of the ecological status. The modalities for this monitoring are stated in the grand ducal Regulation of 30 December 2010 (règlement grand-ducal you 30 décembre 2010 concernant l 'évaluation of the dimension d' eau de surface).

  • The chemical status of the surface water bodies is assessed as being good or failing to achieve good chemical status. The assessment of the chemical status for the second river basin management plan is based on the list of substances of directive 2008/105/EC and the environmental quality standards established by the new directive 2013/39/EC. The assessment without the ubiquist substances permita to get a differentiated picture of the actual situation.

  • The hydromorphological status was determined by a monitoring compliant with the Water Framework Directive (Directive 2000/60/EU). The elaboration of a structural quality mapping is one part of this monitoring. Within the scope of the work on the structural quality mapping, a total of 31 parameters in the area of the river bed, the river bank and the floodplain are assessed so that the structural quality mapping contains detailed information on the river morphology and the river continuity. In this case, the evaluation of the mapped sections is based on five classes. The results of the evaluation were aggregated into an overall evaluation per mapped section.

  • The hydromorphological status was determined by a monitoring compliant with the Water Framework Directive (Directive 2000/60/EU). The elaboration of a structural quality mapping is one part of this monitoring. Within the scope of the work on the structural quality mapping, a total of 31 parameters in the area of the river bed, the river bank and the floodplain are assessed so that the structural quality mapping contains detailed information on the river morphology and the river continuity. In this case, the evaluation of the mapped sections is based on seven classes. The results of the evaluation were aggregated into an overall evaluation per mapped section.

  • According to the water framework directive (Directive 2000/60/CE), the biological parameter fish are monitored in surface water bodies in order to determine the ecological status. Fish react sensitively to the continuity and the hydrological flow of surface water. Fish are therefor sampled in the SWB which have deficits here. The methodology applied for sampling is the standard NF EN 14962:2006 "water quality − guidance on the scope and selection of fish sampling methods".

  • The chemical status of the surface water bodies is assessed as being good or failing to achieve good chemical status. The assessment of the chemical status for the second river basin management plan is based on the list of substances of directive 2008/105/EC as well as its environmental quality standards. The assessment without the ubiquist substances permita to get a differentiated picture of the actual situation.