Member State report / Art9 / 2012 / D4 / Belgium / NE Atlantic: Greater North Sea
Report type | Member State report to Commission |
MSFD Article | Art. 9 Determination of GES (and Art. 17 updates) |
Report due | 2012-10-15 |
GES Descriptor | D4 Food webs/D1 Ecosystems |
Member State | Belgium |
Region/subregion | NE Atlantic: Greater North Sea |
Reported by | FPS Health, Food Chain safety and Environment - Service Marine environment |
Report date | 2012-08-16 |
Report access | ANSBE_MSFD9GES_20130314.xml |
GES component |
D4
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1.7 Ecosystem structure |
1.7.1 Composition ecosystem |
1.7.1 Composition ecosystem |
4.1 Productivity (production per unit biomass) of key species or trophic groups |
4.1.1 Productivity of key predators |
4.2 Proportion of selected species at the top of food webs |
4.2.1 Large fish by weight |
4.3 Abundance/distribution of key trophic groups/species |
4.3.1 Abundance trends of selected groups/species |
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Method used |
ANS-BE-MS-1: Conform the Directive, GES and the environmental targets for the Belgian marine waters are defined on the basis of the eleven qualitative descriptors listed in Annex I of the Directive. The definition of GES is expressed in a qualitative description of what GES would look like when achieved for each of the descriptors. This is then underpinned by a set of more detailed quantitative environmental targets based on established environmental thresholds/limits for state, pressure or impact (Art. 10). Where quantitative environmental thresholds could not be set, trend-based or qualitative thresholds were used. The complete package of GES and environmental targets needs to give a complete and balanced overview. |
ANS-BE-MS-1: Conform the Directive, GES and the environmental targets for the Belgian marine waters are defined on the basis of the eleven qualitative descriptors listed in Annex I of the Directive. The definition of GES is expressed in a qualitative description of what GES would look like when achieved for each of the descriptors. This is then underpinned by a set of more detailed quantitative environmental targets based on established environmental thresholds/limits for state, pressure or impact (Art. 10). Where quantitative environmental thresholds could not be set, trend-based or qualitative thresholds were used. The complete package of GES and environmental targets needs to give a complete and balanced overview. |
ANS-BE-MS-1: Conform the Directive, GES and the environmental targets for the Belgian marine waters are defined on the basis of the eleven qualitative descriptors listed in Annex I of the Directive. The definition of GES is expressed in a qualitative description of what GES would look like when achieved for each of the descriptors. This is then underpinned by a set of more detailed quantitative environmental targets based on established environmental thresholds/limits for state, pressure or impact (Art. 10). Where quantitative environmental thresholds could not be set, trend-based or qualitative thresholds were used. The complete package of GES and environmental targets needs to give a complete and balanced overview. |
ANS-BE-MS-1: Conform the Directive, GES and the environmental targets for the Belgian marine waters are defined on the basis of the eleven qualitative descriptors listed in Annex I of the Directive. The definition of GES is expressed in a qualitative description of what GES would look like when achieved for each of the descriptors. This is then underpinned by a set of more detailed quantitative environmental targets based on established environmental thresholds/limits for state, pressure or impact (Art. 10). Where quantitative environmental thresholds could not be set, trend-based or qualitative thresholds were used. The complete package of GES and environmental targets needs to give a complete and balanced overview. |
ANS-BE-MS-1: Conform the Directive, GES and the environmental targets for the Belgian marine waters are defined on the basis of the eleven qualitative descriptors listed in Annex I of the Directive. The definition of GES is expressed in a qualitative description of what GES would look like when achieved for each of the descriptors. This is then underpinned by a set of more detailed quantitative environmental targets based on established environmental thresholds/limits for state, pressure or impact (Art. 10). Where quantitative environmental thresholds could not be set, trend-based or qualitative thresholds were used. The complete package of GES and environmental targets needs to give a complete and balanced overview. |
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Marine reporting units |
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Feature |
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Criterion/indicator |
D4 |
1.7 |
1.7.1 |
1.7.1 |
4.1 |
4.1.1 |
4.2 |
4.2.1 |
4.3 |
4.3.1 |
GES description |
All elements of the marine food webs, to the extent that they are known, occur at normal abundance and diversity and levels capable of ensuring the long-term abundance of the species and the retention of their full reproductive capacity |
Diversity within the different ecosystem components (i.e. plankton, benthos, fish, seabirds and marine mammals) is maintained. |
The habitat types are structurally and functionally diverse and productive. |
Viable species populations are maintained for the key long-lived, slowly reproducing species, as well as for the top predator species in all habitat types. |
Viable species populations are maintained for the key long-lived, slowly reproducing species, as well as for the top predator species in all habitat types. |
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Threshold values |
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Threshold value unit |
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Proportion of area to achieve threshold value |
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Reference point type |
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Baseline |
Initial Assessment 2012
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Initial Assessment 2012
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Initial Assessment 2012
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Initial Assessment 2012
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Initial Assessment 2012
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Assessment method |
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Development status |