Member State report / Art8 / 2018 / D1-B / Belgium / NE Atlantic: Greater North Sea
Report type | Member State report to Commission |
MSFD Article | Art. 8 Initial assessment (and Art. 17 updates) |
Report due | 2018-10-15 |
GES Descriptor | D1 Birds |
Member State | Belgium |
Region/subregion | NE Atlantic: Greater North Sea |
Reported by | RBINS - Scientific Service MUMM |
Report date | 2020-01-14 |
Report access | ART8_GES_BE_20200110.xml |
Greater North Sea, incl. the Kattegat and the English Channel (ANS)
GES component |
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Feature |
Benthic-feeding birds
|
Grazing birds
|
Grazing birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Wading birds
|
Wading birds
|
Wading birds
|
Wading birds
|
Wading birds
|
Wading birds
|
Wading birds
|
Element |
Somateria mollissima |
Anas platyrhynchos |
Cygnus olor |
Alca torda |
Cepphus grylle |
Fratercula arctica |
Mergus serrator |
Morus bassanus |
Phalacrocorax aristotelis |
Phalacrocorax carbo |
Uria aalge |
Fulmarus glacialis |
Larus argentatus |
Larus fuscus |
Larus marinus |
Larus melanocephalus |
Larus ridibundus |
Rissa tridactyla |
Stercorarius parasiticus |
Stercorarius skua |
Sterna dougallii |
Sterna hirundo |
Sterna paradisaea |
Sterna sandvicensis |
Sternula albifrons |
Charadrius alexandrinus |
Charadrius hiaticula |
Haematopus ostralegus |
Larus canus |
Platalea leucorodia |
Recurvirostra avosetta |
Tadorna tadorna |
Element code |
137074 |
148791 |
159090 |
137128 |
137130 |
137131 |
159098 |
148776 |
137178 |
137179 |
137133 |
137195 |
137138 |
137142 |
137146 |
137147 |
137149 |
137156 |
137172 |
137174 |
137160 |
137162 |
137165 |
137166 |
567480 |
212611 |
212619 |
147436 |
137141 |
416678 |
212721 |
232042 |
Element code source |
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Element 2 |
||||||||||||||||||||||||||||||||
Element 2 code |
||||||||||||||||||||||||||||||||
Element 2 code source |
||||||||||||||||||||||||||||||||
Element source |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
OSPAR |
Criterion |
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
D1C3
|
Parameter |
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Parameter other |
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Breeding abundance
|
Threshold value upper |
||||||||||||||||||||||||||||||||
Threshold value lower |
||||||||||||||||||||||||||||||||
Threshold qualitative |
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Stable population
|
Threshold value source |
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
OSPAR Convention
|
Threshold value source other |
||||||||||||||||||||||||||||||||
Value achieved upper |
||||||||||||||||||||||||||||||||
Value achieved lower |
||||||||||||||||||||||||||||||||
Value unit |
||||||||||||||||||||||||||||||||
Value unit other |
||||||||||||||||||||||||||||||||
Proportion threshold value |
||||||||||||||||||||||||||||||||
Proportion value achieved |
||||||||||||||||||||||||||||||||
Proportion threshold value unit |
||||||||||||||||||||||||||||||||
Trend |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Parameter achieved |
Yes |
No |
No |
Yes |
Yes |
Yes |
No |
Yes |
No |
Yes |
Yes |
No |
No |
Yes |
Yes |
Yes |
No |
No |
No |
Yes |
Yes |
No |
Yes |
Yes |
Yes |
No |
Yes |
No |
No |
Yes |
No |
Yes |
Description parameter |
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
OSPAR assessment
|
Related indicator |
||||||||||||||||||||||||||||||||
Criteria status |
Good |
Not good |
Not good |
Good |
Good |
Good |
Not good |
Good |
Not good |
Good |
Good |
Not good |
Not good |
Good |
Good |
Good |
Not good |
Not good |
Not good |
Good |
Good |
Not good |
Good |
Good |
Good |
Not good |
Good |
Not good |
Not good |
Good |
Not good |
Good |
Description criteria |
||||||||||||||||||||||||||||||||
Element status |
Good |
Not good |
Not good |
Good |
Good |
Good |
Not good |
Good |
Not good |
Good |
Good |
Not good |
Not good |
Good |
Good |
Good |
Not good |
Not good |
Not good |
Good |
Good |
Not good |
Good |
Good |
Good |
Not good |
Good |
Not good |
Not good |
Good |
Not good |
Good |
Description element |
Common Eider
|
Mallard
|
Mute Swan
|
Razorbill
|
Black guillemot
|
Puffin
|
Red-breasted merganser
|
Northern gannet
|
European shag
|
Great cormorant
|
Common guillemot
|
Northern Fulmar
|
Zilvermeeuw - Herring gull
|
Kleine mantelmeeuw - Lesser black-backed gull
|
Great black-backed gull
|
Mediterranean gull
|
Kokmeeuw - Black-headed gull
|
Black-legged kittiwake
|
Arctic skua
|
Great skua
|
Roseate tern
|
Visdief - common tern
|
Arctic tern
|
Grote stern - sandwich tern
|
Dwergstern - little tern
|
Kentish plover
|
Ringed plover
|
Oystercatcher
|
Common gull
|
Eurasian spoonbill
|
Pied avocet
|
Shelduck
|
Integration rule type parameter |
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description parameter |
||||||||||||||||||||||||||||||||
Integration rule type criteria |
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description criteria |
||||||||||||||||||||||||||||||||
GES extent threshold |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
GES extent achieved |
100.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
47.00 |
47.00 |
47.00 |
47.00 |
47.00 |
47.00 |
47.00 |
47.00 |
47.00 |
47.00 |
47.00 |
47.00 |
47.00 |
47.00 |
40.00 |
40.00 |
40.00 |
40.00 |
40.00 |
40.00 |
40.00 |
||
GES extent unit |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
GES achieved |
GES achieved |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
Description overall status |
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Breeding seabirds: In the three investigated OSPAR regions (Arctic waters, North Sea and Celtic Sea), so also in the North Sea region in which Belgium is located, the number of breeding seabirds has fallen sharply: more than 25% of species are currently below the reference level. Since 2005, no good OSPAR region has achieved good environmental status in the North Sea since 2000. Fish-eating species that forage close to the surface of the water are doing poorly.
|
Assessments period |
2014 |
2014 |
2014 |
2014 |
2014 |
2014 |
2014 |
2014 |
2014 |
2014 |
2014 |
2014 |
2014 |
2014 |
2014 |
2014 |
2014 |
2014 |
2014 |
2014 |
2014 |
2014 |
2014 |
2014 |
2014 |
2014 |
2014 |
2014 |
2014 |
2014 |
2014 |
2014 |
Related pressures |
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Related targets |
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Belgian Part of the North Sea (ANS-BE-MS-1)
GES component |
D1-B
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D1-B
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D1-B
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D1-B
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D1-B
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D1-B
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D1-B
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D1-B
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D1-B
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D1-B
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D1-B
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D1-B
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D1-B
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---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Feature |
Benthic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Wading birds
|
Wading birds
|
Wading birds
|
Element |
Melanitta spp. |
Alca torda |
Gavia sp. |
Morus bassanus |
Podiceps cristatus |
Uria aalge |
Hydrocoloeus minutus |
Larus marinus |
Rissa tridactyla |
Sterna hirundo |
Larus argentatus |
Larus canus |
Larus fuscus |
Element code |
137002 |
137128 |
137057 |
148776 |
137182 |
137133 |
567449 |
137146 |
137156 |
137162 |
137138 |
137141 |
137142 |
Element code source |
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
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Species (D1) http://www.marinespecies.org/
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Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
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Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Element 2 |
|||||||||||||
Element 2 code |
|||||||||||||
Element 2 code source |
|||||||||||||
Element source |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
Criterion |
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
D1C2
|
Parameter |
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Parameter other |
Abundance of non-scavengers
|
Abundance of non-scavengers
|
Abundance of non-scavengers
|
Abundance of non-scavengers
|
Abundance of non-scavengers
|
Abundance of non-scavengers
|
Abundance of non-scavengers
|
Abundance of scavengers
|
Abundance of scavengers
|
Abundance of non-scavengers
|
Abundance of scavengers
|
Abundance of scavengers
|
Abundance of scavengers
|
Threshold value upper |
4786.96 |
0.32 |
0.25 |
0.39 |
0.39 |
1.59 |
0.24 |
0.27 |
0.65 |
0.14 |
0.19 |
0.41 |
0.66 |
Threshold value lower |
|||||||||||||
Threshold qualitative |
|||||||||||||
Threshold value source |
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Threshold value source other |
National, long term average abundance
|
National, long term average abundance
|
National, long term average abundance
|
National, long term average abundance
|
National, long term average abundance
|
National, long term average abundance
|
National, long term average abundance
|
National, long term average abundance
|
National, long term average abundance
|
National, long term average abundance
|
National, long term average abundance
|
National, long term average abundance
|
National, long term average abundance
|
Value achieved upper |
1224.8 |
0.6 |
0.24 |
0.36 |
0.73 |
1.79 |
0.37 |
0.26 |
1.11 |
0.18 |
0.23 |
0.69 |
1.06 |
Value achieved lower |
618.8 |
0.43 |
0.08 |
0.2 |
0.48 |
1.26 |
0.23 |
0.1 |
0.71 |
0.05 |
0.04 |
0.28 |
0.43 |
Value unit |
(number of) individuals
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Value unit other |
N/km2
|
N/km2
|
N/km2
|
N/km2
|
N/km2
|
N/km2
|
N/km2
|
N/km2
|
N/km2
|
N/km2
|
N/km2
|
N/km2
|
|
Proportion threshold value |
|||||||||||||
Proportion value achieved |
|||||||||||||
Proportion threshold value unit |
|||||||||||||
Trend |
Improving |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Improving |
Unknown |
Unknown |
Unknown |
Parameter achieved |
No |
Yes |
No |
Unknown |
Yes |
Yes |
Yes |
Yes |
No |
Yes |
Yes |
Yes |
Yes |
Description parameter |
Non-scavenger: not good if five-year average lower than the long-term average for five consecutive years. ParameterAchieved refers to situation 2016. (in the period 2011-2016: 0 years good).
|
Non-scavenger: not good if five-year average lower than the long-term average for five consecutive years. ParameterAchieved refers to situation 2016. (in the period 2011-2016: 6 years good)
|
Non-scavenger: not good if five-year average lower than the long-term average for five consecutive years. ParameterAchieved refers to situation 2016. (in the period 2011-2016: 0 years good).
|
Non-scavenger: not good if five-year average is lower than the long-term average for five consecutive years. Parameter Achieved refers to situation in 2016. (in the period 2011-2014: 0 years good).
|
Non-scavenger: not good if five-year average is lower than the long-term average for five consecutive years. Parameter Achieved refers to situation in 2016. (in the period 2011-2016: 6 years good).
|
Non-scavenger: not good if five-year average is lower than the long-term average for five consecutive years. Parameter Achieved refers to situation in 2016. (in the period 2011-2016: 2 years good).
|
Non-scavenger: not good if five-year average lower than the long-term average for five consecutive years. ParameterAchieved refers to situation 2016. (in the period 2011-2016: 5 years good).
|
Scavenger: not good if five-year average is higher than the long-term average for five consecutive years. Parameter Achieved refers to situation in 2016. (in the period 2011-2016: 6 years good).
|
Scavenger: not good if five-year average is higher than the long-term average for five consecutive years. Parameter Achieved refers to situation in 2016. (in the period 2011-2016: 0 years good).
|
Non-scavenger: not good if five-year average is lower than the long-term average for five consecutive years. Parameter Achieved refers to situation in 2016. (in the period 2011-2016: 2 years good). Decline since 2010 due to lack of predator-free breeding habitat.
|
Scavenger: not good if five-year average is higher than the long-term average for five consecutive years. Parameter Achieved refers to situation in 2016. (in the period 2011-2016: 4 years good).
|
Scavenger: not good if five-year average is higher than the long-term average for five consecutive years. Parameter Achieved refers to situation in 2016. (in the period 2011-2016: 1 year good).
|
Scavenger: not good if five-year average is higher than the long-term average for five consecutive years. Parameter Achieved refers to situation in 2016. (in the period 2011-2016: 2 years good).
|
Related indicator |
|||||||||||||
Criteria status |
Not good |
Good |
Not good |
Unknown |
Good |
Good |
Good |
Unknown |
Unknown |
Good |
Unknown |
Unknown |
Unknown |
Description criteria |
|||||||||||||
Element status |
Not good |
Good |
Not good |
Unknown |
Good |
Good |
Good |
Unknown |
Unknown |
Good |
Unknown |
Unknown |
Unknown |
Description element |
Non-scavenger (Surf scoters)
|
Non-scavenger (Razorbill)
|
Non-scavenger(Loon)
|
Non-scavenger (Northern gannet)
|
Non-scavenger (Great crested grebe)
|
Non-scavenger (Common murre)
|
Non-scavenger (Little gull)
|
Scavenger (Great black-backed gull)
|
Scavenger (Black-legged kittiwake)
|
Non-scavenger (Common tern)
|
Scavenger(Herring gull)
|
Scavenger (Common gull)
|
Scavenger (Lesser black-backed gull)
|
Integration rule type parameter |
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description parameter |
|||||||||||||
Integration rule type criteria |
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description criteria |
|||||||||||||
GES extent threshold |
|||||||||||||
GES extent achieved |
|||||||||||||
GES extent unit |
|||||||||||||
GES achieved |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Description overall status |
Density of sesabirds: The good environmental status of the non-necrophagous bird species on the BDZ for the period 2011-2016 was achieved each year, although the majority of species show a prolonged decline. The five necrophagous species, whose number was considered unnaturally high, declined sharply, while good environmental status was not achieved in 4 out of 6 years because the population size was higher than the long-term average. It was not possible to evaluate whether the 5 year averages were not less than the minima laid down in the Birds Directive for the favourable status of conservation. In view of the sharp decline in a number of species, it is not possible to give a ruling on the status of the bait.
|
Density of sesabirds: The good environmental status of the non-necrophagous bird species on the BDZ for the period 2011-2016 was achieved each year, although the majority of species show a prolonged decline. The five necrophagous species, whose number was considered unnaturally high, declined sharply, while good environmental status was not achieved in 4 out of 6 years because the population size was higher than the long-term average. It was not possible to evaluate whether the 5 year averages were not less than the minima laid down in the Birds Directive for the favourable status of conservation. In view of the sharp decline in a number of species, it is not possible to give a ruling on the status of the bait.
|
Density of sesabirds: The good environmental status of the non-necrophagous bird species on the BDZ for the period 2011-2016 was achieved each year, although the majority of species show a prolonged decline. The five necrophagous species, whose number was considered unnaturally high, declined sharply, while good environmental status was not achieved in 4 out of 6 years because the population size was higher than the long-term average. It was not possible to evaluate whether the 5 year averages were not less than the minima laid down in the Birds Directive for the favourable status of conservation. In view of the sharp decline in a number of species, it is not possible to give a ruling on the status of the bait.
|
Density of sesabirds: The good environmental status of the non-necrophagous bird species on the BDZ for the period 2011-2016 was achieved each year, although the majority of species show a prolonged decline. The five necrophagous species, whose number was considered unnaturally high, declined sharply, while good environmental status was not achieved in 4 out of 6 years because the population size was higher than the long-term average. It was not possible to evaluate whether the 5 year averages were not less than the minima laid down in the Birds Directive for the favourable status of conservation. In view of the sharp decline in a number of species, it is not possible to give a ruling on the status of the bait.
|
Density of sesabirds: The good environmental status of the non-necrophagous bird species on the BDZ for the period 2011-2016 was achieved each year, although the majority of species show a prolonged decline. The five necrophagous species, whose number was considered unnaturally high, declined sharply, while good environmental status was not achieved in 4 out of 6 years because the population size was higher than the long-term average. It was not possible to evaluate whether the 5 year averages were not less than the minima laid down in the Birds Directive for the favourable status of conservation. In view of the sharp decline in a number of species, it is not possible to give a ruling on the status of the bait.
|
Density of sesabirds: The good environmental status of the non-necrophagous bird species on the BDZ for the period 2011-2016 was achieved each year, although the majority of species show a prolonged decline. The five necrophagous species, whose number was considered unnaturally high, declined sharply, while good environmental status was not achieved in 4 out of 6 years because the population size was higher than the long-term average. It was not possible to evaluate whether the 5 year averages were not less than the minima laid down in the Birds Directive for the favourable status of conservation. In view of the sharp decline in a number of species, it is not possible to give a ruling on the status of the bait.
|
Density of sesabirds: The good environmental status of the non-necrophagous bird species on the BDZ for the period 2011-2016 was achieved each year, although the majority of species show a prolonged decline. The five necrophagous species, whose number was considered unnaturally high, declined sharply, while good environmental status was not achieved in 4 out of 6 years because the population size was higher than the long-term average. It was not possible to evaluate whether the 5 year averages were not less than the minima laid down in the Birds Directive for the favourable status of conservation. In view of the sharp decline in a number of species, it is not possible to give a ruling on the status of the bait.
|
Density of sesabirds: The good environmental status of the non-necrophagous bird species on the BDZ for the period 2011-2016 was achieved each year, although the majority of species show a prolonged decline. The five necrophagous species, whose number was considered unnaturally high, declined sharply, while good environmental status was not achieved in 4 out of 6 years because the population size was higher than the long-term average. It was not possible to evaluate whether the 5 year averages were not less than the minima laid down in the Birds Directive for the favourable status of conservation. In view of the sharp decline in a number of species, it is not possible to give a ruling on the status of the bait.
|
Density of sesabirds: The good environmental status of the non-necrophagous bird species on the BDZ for the period 2011-2016 was achieved each year, although the majority of species show a prolonged decline. The five necrophagous species, whose number was considered unnaturally high, declined sharply, while good environmental status was not achieved in 4 out of 6 years because the population size was higher than the long-term average. It was not possible to evaluate whether the 5 year averages were not less than the minima laid down in the Birds Directive for the favourable status of conservation. In view of the sharp decline in a number of species, it is not possible to give a ruling on the status of the bait.
|
Density of sesabirds: The good environmental status of the non-necrophagous bird species on the BDZ for the period 2011-2016 was achieved each year, although the majority of species show a prolonged decline. The five necrophagous species, whose number was considered unnaturally high, declined sharply, while good environmental status was not achieved in 4 out of 6 years because the population size was higher than the long-term average. It was not possible to evaluate whether the 5 year averages were not less than the minima laid down in the Birds Directive for the favourable status of conservation. In view of the sharp decline in a number of species, it is not possible to give a ruling on the status of the bait.
|
Density of sesabirds: The good environmental status of the non-necrophagous bird species on the BDZ for the period 2011-2016 was achieved each year, although the majority of species show a prolonged decline. The five necrophagous species, whose number was considered unnaturally high, declined sharply, while good environmental status was not achieved in 4 out of 6 years because the population size was higher than the long-term average. It was not possible to evaluate whether the 5 year averages were not less than the minima laid down in the Birds Directive for the favourable status of conservation. In view of the sharp decline in a number of species, it is not possible to give a ruling on the status of the bait.
|
Density of sesabirds: The good environmental status of the non-necrophagous bird species on the BDZ for the period 2011-2016 was achieved each year, although the majority of species show a prolonged decline. The five necrophagous species, whose number was considered unnaturally high, declined sharply, while good environmental status was not achieved in 4 out of 6 years because the population size was higher than the long-term average. It was not possible to evaluate whether the 5 year averages were not less than the minima laid down in the Birds Directive for the favourable status of conservation. In view of the sharp decline in a number of species, it is not possible to give a ruling on the status of the bait.
|
Density of sesabirds: The good environmental status of the non-necrophagous bird species on the BDZ for the period 2011-2016 was achieved each year, although the majority of species show a prolonged decline. The five necrophagous species, whose number was considered unnaturally high, declined sharply, while good environmental status was not achieved in 4 out of 6 years because the population size was higher than the long-term average. It was not possible to evaluate whether the 5 year averages were not less than the minima laid down in the Birds Directive for the favourable status of conservation. In view of the sharp decline in a number of species, it is not possible to give a ruling on the status of the bait.
|
Assessments period |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
2011-2016 |
Related pressures |
|
|
|
|
|
|
|
|
|
|
|
|
|
Related targets |
|
|
|
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