Member State report / Art10 / 2018 / D1-M / Netherlands / NE Atlantic: Greater North Sea
Report type | Member State report to Commission |
MSFD Article | Art. 10 Environmental targets (and Art. 17 updates) |
Report due | 2018-10-15 |
GES Descriptor | D1 Mammals |
Member State | Netherlands |
Region/subregion | NE Atlantic: Greater North Sea |
Reported by | Rijkswaterstaat Centre for Water management, Ministry of infrastructure and the environment |
Report date | 2019-04-15 |
Report access | XML_ART10_201904091515.xml |
Target code |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T2 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T3 |
ANSNL-D1T4 |
ANSNL-D1T4 |
ANSNL-D1T4 |
ANSNL-D1T8 |
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Target description |
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
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Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
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Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
|
Restoration of rest for marine mammals and birds by reducing fishing in the Vlakte van de Raan and the North Sea Coastal Zone (under the VIBEG agreement).
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
|
Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
|
Preparing and implementing the management plans for Natura 2000 sites at sea.
|
Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
|
Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Preparing and implementing the management plans for Natura 2000 sites at sea.
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Implementation of mitigation measures in the context of the 2012 Porpoise Protection Plan, including: - By-catch monitoring and research into the application of mitigation measures (pingers) - Preventing or reducing the harmful effects of underwater noise on porpoise populations (NB Act) - Further investigation into the effects around construction and exploitation of offshore wind farms on the porpoise populations (in the context of WOZEP).
|
Implementation of mitigation measures in the context of the 2012 Porpoise Protection Plan, including: - By-catch monitoring and research into the application of mitigation measures (pingers) - Preventing or reducing the harmful effects of underwater noise on porpoise populations (NB Act) - Further investigation into the effects around construction and exploitation of offshore wind farms on the porpoise populations (in the context of WOZEP).
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Implementation of mitigation measures in the context of the 2012 Porpoise Protection Plan, including: - By-catch monitoring and research into the application of mitigation measures (pingers) - Preventing or reducing the harmful effects of underwater noise on porpoise populations (NB Act) - Further investigation into the effects around construction and exploitation of offshore wind farms on the porpoise populations (in the context of WOZEP).
|
Further research into cumulative effects in OSPAR
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Feature(s) |
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GES components |
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Timescale |
202407 |
202407 |
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202407 |
202407 |
202407 |
202407 |
202407 |
202407 |
202407 |
202407 |
202407 |
202407 |
Update date |
201807 |
201807 |
201807 |
201807 |
201807 |
201807 |
201807 |
201807 |
201807 |
201807 |
201807 |
201807 |
201807 |
201807 |
201807 |
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201807 |
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201807 |
201807 |
201807 |
201807 |
201807 |
201807 |
201807 |
201807 |
201807 |
201807 |
201807 |
201807 |
Update type |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Same as 2012 definition |
Marine reporting unit |
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Element |
Alca torda |
Benthic feeders breeding |
Benthic feeders non breeding |
Chroicocephalus ridibundus |
Fratercula arctica |
Fulmarus glacialis |
Grazing feeders non breeding |
Halichoerus grypus |
Halichoerus grypus |
Halichoerus grypus |
Larus argentatus |
Larus canus |
Larus fuscus |
Larus marinus |
Morus bassanus |
Phalacrocorax aristotelis |
Phalacrocorax carbo |
Phoca vitulina |
Phoca vitulina |
Phocoena phocoena |
Phocoena phocoena |
Rissa tridactyla |
Stercorarius parasiticus |
Stercorarius skua |
Sterna albifrons |
Sterna dougallii |
Sterna hirundo |
Sterna paradisaea |
Sterna sandvicensis |
Surface feeders breeding |
Surface feeders non breeding |
Uria aalge |
Wading feeders breeding |
Wading feeders non breeding |
Water column feeders breeding |
Water column feeders non breeding |
Benthic feeders breeding |
Benthic feeders non breeding |
Coastal Zone Sand (NL) |
Demersal fish community |
Dogger Bank Sand (NL) |
Fratercula arctica |
Frysian Front Sand (NL) |
Fulmarus glacialis |
Grazing feeders non breeding |
H1110b |
H1110c |
H1170 |
HabBenCircalitCoarSed |
HabBenCircalitMud |
HabBenCircalitSand |
HabBenOffshCoarSed |
HabBenOffshMud |
HabBenOffshSand |
Halichoerus grypus |
Halichoerus grypus |
Halichoerus grypus |
Larus argentatus |
Larus canus |
Larus fuscus |
Larus marinus |
Morus bassanus |
Offshore Sand (NL) |
Oyster Banks Mud (NL) |
Phalacrocorax aristotelis |
Phalacrocorax carbo |
Phoca vitulina |
Phoca vitulina |
Phocoena phocoena |
Phocoena phocoena |
Rissa tridactyla |
Sensitive fish species |
Stercorarius parasiticus |
Stercorarius skua |
Sterna dougallii |
Sterna hirundo |
Sterna paradisaea |
Sterna sandvicensis |
Sternula albifrons |
Surface feeders breeding |
Surface feeders non breeding |
Uria aalge |
Wading feeders breeding |
Wading feeders non breeding |
Water column feeders breeding |
Water column feeders non breeding |
Phocoena phocoena |
Phocoena phocoena |
Phocoena phocoena |
Phocoena phocoena |
Element 2 |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Parameter |
Other
|
Abundance
|
Abundance
|
Other
|
Other
|
Other
|
Abundance
|
Abundance
|
Distribution (spatial)
|
Fecundity rate
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Abundance
|
Distribution (spatial)
|
Abundance
|
Distribution (spatial)
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Abundance
|
Abundance
|
Other
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Habitat condition
|
Size distribution
|
Habitat condition
|
Other
|
Habitat condition
|
Other
|
Abundance
|
Habitat condition
|
Habitat condition
|
Habitat condition
|
Habitat condition
|
Habitat condition
|
Habitat condition
|
Habitat condition
|
Habitat condition
|
Habitat condition
|
Abundance
|
Distribution (spatial)
|
Fecundity rate
|
Other
|
Other
|
Other
|
Other
|
Other
|
Habitat condition
|
Habitat condition
|
Other
|
Other
|
Abundance
|
Distribution (spatial)
|
Abundance
|
Distribution (spatial)
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Abundance
|
Abundance
|
Other
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Abundance
|
Distribution (spatial)
|
Mortality rate / Mortality rate from fishing (F)
|
Mortality rate / Mortality rate from fishing (F)
|
Parameter - other |
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Proportion failing to spawn.
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
Breeding Success
|
|||||||||||||||||||||||||||||||||||||||||||||||||||
Target value |
3.0 |
75.0 |
75.0 |
3.0 |
3.0 |
3.0 |
75.0 |
-1.0 |
3.0 |
3.0 |
3.0 |
3.0 |
3.0 |
3.0 |
3.0 |
3.0 |
3.0 |
3.0 |
3.0 |
3.0 |
3.0 |
3.0 |
3.0 |
75.0 |
75.0 |
3.0 |
75.0 |
75.0 |
75.0 |
75.0 |
75.0 |
75.0 |
1.0 |
3.0 |
3.0 |
75.0 |
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
1.0 |
-1.0 |
3.0 |
3.0 |
3.0 |
3.0 |
3.0 |
3.0 |
3.0 |
3.0 |
1.0 |
3.0 |
3.0 |
3.0 |
3.0 |
3.0 |
3.0 |
3.0 |
75.0 |
75.0 |
3.0 |
75.0 |
75.0 |
75.0 |
75.0 |
1.0 |
1.0 |
|||||||||||||||||||
Value achieved - upper |
3.0 |
100.0 |
55.6 |
2.0 |
4.0 |
4.0 |
88.9 |
1.0 |
1.0 |
9.0 |
4.0 |
2.0 |
2.0 |
2.0 |
4.0 |
4.0 |
4.0 |
1.0 |
1.0 |
2.0 |
2.0 |
4.0 |
4.0 |
4.0 |
3.0 |
4.0 |
2.0 |
58.3 |
80.0 |
4.0 |
50.0 |
75.0 |
80.0 |
66.7 |
100.0 |
55.6 |
4.0 |
4.0 |
88.9 |
1.0 |
1.0 |
9.0 |
4.0 |
2.0 |
2.0 |
2.0 |
4.0 |
4.0 |
4.0 |
1.0 |
1.0 |
2.0 |
2.0 |
4.0 |
4.0 |
3.0 |
4.0 |
2.0 |
4.0 |
58.3 |
80.0 |
4.0 |
50.0 |
75.0 |
80.0 |
66.7 |
0.58 |
0.58 |
||||||||||||||||||||||
Value achieved - lower |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Value unit |
Other
|
percentage
|
percentage
|
Other
|
Other
|
Other
|
percentage
|
Other
|
Other
|
percentage
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
percentage
|
percentage
|
Other
|
percentage
|
percentage
|
percentage
|
percentage
|
percentage
|
percentage
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
percentage
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
percentage
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
percentage
|
percentage
|
Other
|
percentage
|
percentage
|
percentage
|
percentage
|
Other
|
Other
|
percentage
|
percentage
|
Value unit - other |
Broods per 6 years
|
Broods per 6 years
|
Broods per 6 years
|
Broods per 6 years
|
Trend indicator
|
Trend indicator
|
Broods per 6 years
|
Broods per 6 years
|
Broods per 6 years
|
Broods per 6 years
|
Broods per 6 years
|
Broods per 6 years
|
Broods per 6 years
|
Trend indicator
|
Trend indicator
|
Trend indicator
|
Trend indicator
|
Broods per 6 years
|
Broods per 6 years
|
Broods per 6 years
|
Broods per 6 years
|
Broods per 6 years
|
Broods per 6 years
|
Broods per 6 years
|
Broods per 6 years
|
Broods per 6 years
|
trend indicator
|
Trend indicator
|
trend indicator
|
Broods per 6 years
|
trend indicator
|
Broods per 6 years
|
trend indicator
|
trend indicator
|
trend indicator
|
trend indicator
|
trend indicator
|
trend indicator
|
trend indicator
|
trend indicator
|
trend indicator
|
Trend indicator
|
Trend indicator
|
Broods per 6 years
|
Broods per 6 years
|
Broods per 6 years
|
Broods per 6 years
|
Broods per 6 years
|
trend indicator
|
trend indicator
|
Broods per 6 years
|
Broods per 6 years
|
Trend indicator
|
Trend indicator
|
Trend indicator
|
Trend indicator
|
Broods per 6 years
|
Trend indicator
|
Broods per 6 years
|
Broods per 6 years
|
Broods per 6 years
|
Broods per 6 years
|
Broods per 6 years
|
Broods per 6 years
|
Broods per 6 years
|
Broods per 6 years
|
Trend indicator
|
trend indicator
|
||||||||||||||||||||||
Target status |
Target achieved |
Target achieved |
Target not yet achieved |
Target not yet achieved |
Target achieved |
Target achieved |
Target achieved |
Target achieved |
Target achieved |
Target achieved |
Target achieved |
Target not yet achieved |
Target not yet achieved |
Target not yet achieved |
Target not yet achieved |
Target achieved |
Target achieved |
Target achieved |
Target achieved |
Target achieved |
Target achieved |
Target not yet achieved |
Target not yet achieved |
Target achieved |
Target achieved |
Target achieved |
Target achieved |
Target achieved |
Target not yet achieved |
Target not yet achieved |
Target achieved |
Target achieved |
Target not yet achieved |
Target achieved |
Target achieved |
Target not yet achieved |
Target achieved |
Target not yet achieved |
Target not yet achieved |
Target not yet achieved |
Target not yet achieved |
Target achieved |
Target not yet achieved |
Target achieved |
Target achieved |
Target not yet achieved |
Target not yet achieved |
Target not yet achieved |
Target not yet achieved |
Target not yet achieved |
Target not yet achieved |
Target not yet achieved |
Target not yet achieved |
Target not yet achieved |
Target achieved |
Target achieved |
Target achieved |
Target achieved |
Target not yet achieved |
Target not yet achieved |
Target not yet achieved |
Target achieved |
Target achieved |
Target not yet achieved |
Target achieved |
Target achieved |
Target achieved |
Target achieved |
Target achieved |
Target achieved |
Target not yet achieved |
Target not yet achieved |
Target not yet achieved |
Target achieved |
Target achieved |
Target achieved |
Target achieved |
Target not yet achieved |
Target achieved |
Target not yet achieved |
Target achieved |
Target achieved |
Target not yet achieved |
Target achieved |
Target achieved |
Target not yet achieved |
Target achieved |
Target achieved |
Target achieved |
Target achieved |
Assessment period |
1986-2015 |
1992-2014 |
1992-2014 |
1986-2015 |
1986-2015 |
1986-2015 |
1992-2014 |
1992-2014 |
1992-2014 |
1992-2014 |
1986-2015 |
1986-2015 |
1986-2015 |
1986-2015 |
1986-2015 |
1986-2015 |
1986-2015 |
1992-2014 |
1992-2014 |
1994-2016 |
1994-2016 |
1986-2015 |
1986-2015 |
1986-2015 |
1986-2015 |
1986-2015 |
1986-2015 |
1986-2015 |
1986-2015 |
1992-2014 |
1992-2014 |
1986-2015 |
1992-2014 |
1992-2014 |
1992-2014 |
1992-2014 |
1992-2014 |
1992-2014 |
2015-2024 |
1983-2016 |
2015-2024 |
1986-2015 |
2015-2024 |
1986-2015 |
1992-2014 |
2015-2024 |
2015-2024 |
2015-2024 |
2015-2024 |
2015-2024 |
2015-2024 |
2015-2024 |
2015-2024 |
2015-2024 |
1992-2014 |
1992-2014 |
1992-2014 |
1986-2015 |
1986-2015 |
1986-2015 |
1986-2015 |
1986-2015 |
2015-2024 |
2015-2024 |
1986-2015 |
1986-2015 |
1992-2014 |
1992-2014 |
1994-2016 |
1994-2016 |
1986-2015 |
2010-2016 |
1986-2015 |
1986-2015 |
1986-2015 |
1986-2015 |
1986-2015 |
1986-2015 |
1986-2015 |
1992-2014 |
1992-2014 |
1986-2015 |
1992-2014 |
1992-2014 |
1992-2014 |
1992-2014 |
1994-2016 |
1994-2016 |
2013-2013 |
2013-2013 |
Target assessment description |
At least 3 successful broods per 6 years. This threshold applies to all species
|
For each functional group, the population size for at least 75% of the species is above the 1992 threshold value (OSPAR assessment value).
|
For each functional group, the population size for at least 75% of the species is above the 1992 threshold value (OSPAR assessment value).
|
At least 3 successful broods per 6 years. This threshold applies to all species
|
At least 3 successful broods per 6 years. This threshold applies to all species
|
At least 3 successful broods per 6 years. This threshold applies to all species.
|
For each functional group, the population size for at least 75% of the species is above the 1992 threshold value (OSPAR assessment value).
|
At least a stable trend in the grey and common seals population
|
At least a stable trend in the grey and common seals population
|
No decrease in the trend of pupil production to the level where the maximum decrease of 1 % is compared to the latest
assessment
|
At least 3 successful broods per 6 years. This threshold applies to all species
|
At least 3 successful broods per 6 years. This threshold applies to all species
|
At least 3 successful broods per 6 years. This threshold applies to all species
|
At least 3 successful broods per 6 years. This threshold applies to all species
|
At least 3 successful broods per 6 years. This threshold applies to all species
|
At least 3 successful broods per 6 years. This threshold applies to all species
|
At least 3 successful broods per 6 years. This threshold applies to all species
|
At least a stable trend in the grey and common seals population
|
At least a stable trend in the grey and common seals population
|
The censuses of small cetaceans in European Atlantic waters (scans 1994, 2005 and 2016) show stable trends.
|
The censuses of small cetaceans in European Atlantic waters (scans 1994, 2005 and 2016) show stable trends.
|
At least 3 successful broods per 6 years. This threshold applies to all species
|
At least 3 successful broods per 6 years. This threshold applies to all species
|
At least 3 successful broods per 6 years. This threshold applies to all species
|
At least 3 successful broods per 6 years. This threshold applies to all species
|
At least 3 successful broods per 6 years. This threshold applies to all species
|
At least 3 successful broods per 6 years. This threshold applies to all species
|
At least 3 successful broods per 6 years. This threshold applies to all species
|
At least 3 successful broods per 6 years. This threshold applies to all species
|
For each functional group, the population size for at least 75% of the species is above the 1992 threshold value (OSPAR assessment value).
|
For each functional group, the population size for at least 75% of the species is above the 1992 threshold value (OSPAR assessment value).
|
At least 3 successful broods per 6 years. This threshold applies to all species
|
For each functional group, the population size for at least 75% of the species is above the 1992 threshold value (OSPAR assessment value).
|
For each functional group, the population size for at least 75% of the species is above the 1992 threshold value (OSPAR assessment value).
|
For each functional group, the population size for at least 75% of the species is above the 1992 threshold value (OSPAR assessment value).
|
For each functional group, the population size for at least 75% of the species is above the 1992 threshold value (OSPAR assessment value).
|
For each functional group, the population size for at least 75% of the species is above the 1992 threshold value (OSPAR assessment value).
|
For each functional group, the population size for at least 75% of the species is above the 1992 threshold value (OSPAR assessment value).
|
In OSPAR, Margalef index scores have been calculated for various areas within the Southern North Sea. Based on these scores, a comparison between areas is possible, but it is not yet possible to make statements about the status of the areas concerned and the Southern North Sea as a whole. This requires threshold values that have not yet been developed within the OSPAR context.
|
In the International North Sea, there is a recovery in terms of the size composition within the bottom fishing community. Only in the northern part of the Celtic Sea are the target values for recovery met. Target values that are not yet met in various individual survey assessments can, according to recent recovery trends, be achieved by the year 2022 provided that the current level of threat does not increase further. There is no recovery yet in the Southern North Sea.
|
In OSPAR, Margalef index scores have been calculated for various areas within the Southern North Sea. Based on these scores, a comparison between areas is possible, but it is not yet possible to make statements about the status of the areas concerned and the Southern North Sea as a whole. This requires threshold values that have not yet been developed within the OSPAR context.
|
At least 3 successful broods per 6 years. This threshold value applies to all species.
|
In OSPAR, Margalef index scores have been calculated for various areas within the Southern North Sea. Based on these scores, a comparison between areas is possible, but it is not yet possible to make statements about the status of the areas concerned and the Southern North Sea as a whole. This requires threshold values that have not yet been developed within the OSPAR context.
|
At least 3 successful broods per 6 years. This threshold value applies to all species.
|
For each functional group, the population size for at least 75% of the species is above the 1992 threshold value (OSPAR assessment value).
|
Status not yet known because an improvement compared to the T0 (situation in 2015) must be established. No data is currently available for this trend assessment (the next year with benthos monitoring is 2018). However, based on indicative trends, it appears that GMT will not be met in 2018.
|
Status not yet known because an improvement compared to the T0 (situation in 2015) must be established. No data is currently available for this trend assessment (the next year with benthos monitoring is 2018). However, based on indicative trends, it appears that GMT will not be met in 2018.
|
Status not yet known because an improvement compared to the T0 (situation in 2015) must be established. No data is currently available for this trend assessment (the next year with benthos monitoring is 2018). However, based on indicative trends, it appears that GMT will not be met in 2018.
|
Status not yet known because an improvement compared to the T0 (situation in 2015) must be established. No data is currently available for this trend assessment (the next year with benthos monitoring is 2018). However, based on indicative trends, it appears that GMT will not be met in 2018.
|
Status not yet known because an improvement compared to the T0 (situation in 2015) must be established. No data is currently available for this trend assessment (the next year with benthos monitoring is 2018). However, based on indicative trends, it appears that GMT will not be met in 2018.
|
Status not yet known because an improvement compared to the T0 (situation in 2015) must be established. No data is currently available for this trend assessment (the next year with benthos monitoring is 2018). However, based on indicative trends, it appears that GMT will not be met in 2018.
|
Status not yet known because an improvement compared to the T0 (situation in 2015) must be established. No data is currently available for this trend assessment (the next year with benthos monitoring is 2018). However, based on indicative trends, it appears that GMT will not be met in 2018.
|
Status not yet known because an improvement compared to the T0 (situation in 2015) must be established. No data is currently available for this trend assessment (the next year with benthos monitoring is 2018). However, based on indicative trends, it appears that GMT will not be met in 2018.
|
Status not yet known because an improvement compared to the T0 (situation in 2015) must be established. No data is currently available for this trend assessment (the next year with benthos monitoring is 2018). However, based on indicative trends, it appears that GMT will not be met in 2018.
|
At least a stable trend in the grey and common seals population
|
At least a stable trend in the grey and common seals population
|
The number of newly born gray seals in the International North Sea and parts of the Celtic Sea has increased significantly every year since 1992, a trend that continues to this day (2009-2014).
|
At least 3 successful broods per 6 years. This threshold value applies to all species.
|
At least 3 successful broods per 6 years. This threshold value applies to all species.
|
At least 3 successful broods per 6 years. This threshold value applies to all species.
|
At least 3 successful broods per 6 years. This threshold value applies to all species.
|
At least 3 successful broods per 6 years. This threshold value applies to all species.
|
In OSPAR, Margalef index scores have been calculated for various areas within the Southern North Sea. Based on these scores, a comparison between areas is possible, but it is not yet possible to make statements about the status of the areas concerned and the Southern North Sea as a whole. This requires threshold values that have not yet been developed within the OSPAR context.
|
In OSPAR, Margalef index scores have been calculated for various areas within the Southern North Sea. Based on these scores, a comparison between areas is possible, but it is not yet possible to make statements about the status of the areas concerned and the Southern North Sea as a whole. This requires threshold values that have not yet been developed within the OSPAR context.
|
At least 3 successful broods per 6 years. This threshold value applies to all species.
|
At least 3 successful broods per 6 years. This threshold value applies to all species.
|
At least a stable trend in the grey and common seals population
|
At least a stable trend in the grey and common seals population
|
The censuses of small cetaceans in European Atlantic waters (scans 1994, 2005 and 2016) show stable trends.
|
The censuses of small cetaceans in European Atlantic waters (scans 1994, 2005 and 2016) show stable trends.
|
At least 3 successful broods per 6 years. This threshold value applies to all species.
|
There is no evidence of a significant recovery of sensitive fish species in the 2010-2016 period in the regional scale of the North East Atlantic. However, the decline in sensitive fish species has been stopped since 2010, both at the regional scale and at the subregional scale of the international North Sea. Different indicators defining sensitive fish species and different methods of integrating data produced the same conclusions.
|
At least 3 successful broods per 6 years. This threshold value applies to all species.
|
At least 3 successful broods per 6 years. This threshold value applies to all species.
|
At least 3 successful broods per 6 years. This threshold value applies to all species.
|
At least 3 successful broods per 6 years. This threshold value applies to all species.
|
At least 3 successful broods per 6 years. This threshold value applies to all species.
|
At least 3 successful broods per 6 years. This threshold value applies to all species.
|
At least 3 successful broods per 6 years. This threshold value applies to all species.
|
For each functional group, the population size for at least 75% of the species is above the 1992 threshold value (OSPAR assessment value).
|
For each functional group, the population size for at least 75% of the species is above the 1992 threshold value (OSPAR assessment value).
|
At least 3 successful broods per 6 years. This threshold value applies to all species.
|
For each functional group, the population size for at least 75% of the species is above the 1992 threshold value (OSPAR assessment value).
|
For each functional group, the population size for at least 75% of the species is above the 1992 threshold value (OSPAR assessment value).
|
For each functional group, the population size for at least 75% of the species is above the 1992 threshold value (OSPAR assessment value).
|
For each functional group, the population size for at least 75% of the species is above the 1992 threshold value (OSPAR assessment value).
|
The censuses of small cetaceans in European Atlantic waters (scans 1994, 2005 and 2016) show stable trends.
|
The censuses of small cetaceans in European Atlantic waters (scans 1994, 2005 and 2016) show stable trends.
|
On an estimated abundance of 345.400 harbour porpoises in 2013 in the ICES area of the North Sea against the 2000 animals surrounding the effects of entanglement in commercial nets. The estimated by-catch rate for the area where the Dutch North Sea is included lies between 0,36-0.58 %.
|
At OSPAR assessment, a by-catch percentage of less than 1 % was established.
|
Related indicator |
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