Member State report / Art8 / 2018 / D1-F / Denmark / 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 Fish |
Member State | Denmark |
Region/subregion | NE Atlantic: Greater North Sea |
Reported by | Danish Environmental Protection Agency |
Report date | 2019-08-30 |
Report access | DK_ART8_GES_Merge_20190829.xml |
Danish part of Atlantic North Sea from coastline to EEZ (ANS-DK-TOTAL)
GES component |
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Feature |
Coastal fish
|
Coastal fish
|
Coastal fish
|
Coastal fish
|
Deep-sea fish
|
Deep-sea fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Pelagic shelf fish
|
Pelagic shelf fish
|
Element |
Platichthys flesus |
Platichthys flesus |
Zoarces viviparous |
Zoarces viviparous |
Chimaera monstrosa |
Chimaera monstrosa |
Amblyraja radiata |
Amblyraja radiata |
Anarhichas lupus |
Anarhichas lupus |
Dipturus batis |
Dipturus batis |
Hippoglossus hippoglossus |
Hippoglossus hippoglossus |
Lophius piscatorius |
Lophius piscatorius |
Molva molva |
Molva molva |
Mustelus asterias |
Mustelus asterias |
Mustelus mustelus |
Mustelus mustelus |
Phycis blennoides |
Phycis blennoides |
Raja clavata |
Raja clavata |
Raja montagui |
Raja montagui |
Galeorhinus galeus |
Galeorhinus galeus |
Element code |
127141 |
127141 |
127123 |
127123 |
105824 |
105824 |
105865 |
105865 |
126758 |
126758 |
105869 |
105869 |
127138 |
127138 |
126554 |
126554 |
126459 |
126459 |
105821 |
105821 |
105822 |
105822 |
126501 |
126501 |
105883 |
105883 |
105887 |
105887 |
105820 |
105820 |
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/
|
Element 2 |
||||||||||||||||||||||||||||||
Element 2 code |
||||||||||||||||||||||||||||||
Element 2 code source |
||||||||||||||||||||||||||||||
Element source |
ICES |
ICES |
National |
National |
ICES |
ICES |
ICES |
ICES |
ICES |
ICES |
ICES |
ICES |
ICES |
ICES |
ICES |
ICES |
ICES |
ICES |
ICES |
ICES |
ICES |
ICES |
ICES |
ICES |
ICES |
ICES |
ICES |
ICES |
ICES |
ICES |
Criterion |
D1C1
|
D1C2
|
D1C1
|
D1C2
|
D1C1
|
D1C2
|
D1C1
|
D1C2
|
D1C1
|
D1C2
|
D1C1
|
D1C2
|
D1C1
|
D1C2
|
D1C1
|
D1C2
|
D1C1
|
D1C2
|
D1C1
|
D1C2
|
D1C1
|
D1C2
|
D1C1
|
D1C2
|
D1C1
|
D1C2
|
D1C1
|
D1C2
|
D1C1
|
D1C2
|
Parameter |
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Parameter other |
||||||||||||||||||||||||||||||
Threshold value upper |
||||||||||||||||||||||||||||||
Threshold value lower |
||||||||||||||||||||||||||||||
Threshold qualitative |
||||||||||||||||||||||||||||||
Threshold value source |
||||||||||||||||||||||||||||||
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 |
Improving |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Parameter achieved |
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 |
Description parameter |
||||||||||||||||||||||||||||||
Related indicator |
||||||||||||||||||||||||||||||
Criteria status |
Unknown |
Unknown |
Unknown |
Not good |
Unknown |
Not good |
Unknown |
Not good |
Unknown |
Not good |
Unknown |
Not good |
Unknown |
Not good |
Unknown |
Good |
Unknown |
Good |
Unknown |
Not good |
Unknown |
Not good |
Unknown |
Good |
Unknown |
Not good |
Unknown |
Not good |
Unknown |
Not good |
Description criteria |
ICES estimates that for European flounder in the North Sea incl. Skagerrak and Kattegat there is not a clear trend in population density.
|
Data on fishing mortality for eelpout is not included in the assessment.
|
For eelpouts, 19 coastal areas in Denmark have been assessed. Out of these 19 areas, only three sites achieved good environmental status. The condition is therefore characterized as not good.
|
There is no reliable historical by-catch number for rabbit fish and the amount of discards is unknown.
|
The development of the catch rate of rabbit fish indicates a positive trend in population development, but it is not significant. Based on scientific trawl studies.
|
There is no reliable historical by-catch number for the thorny skate and the amount of discards is unknown.
|
Developments in the catch rate of thorny skate indicate a negative trend in stock development, however, it is not significant. Based on scientific trawl surveys.
|
Over the last 10 years, there has been a decline in the fishing mortality rate for wolffish, but since a limit value has not yet been established, it is not possible to quantitatively assess whether it is in good condition.
|
The trend in wolffish catch rates indicates a positive trend in stock development, however it is not significant. Based on scientific trawl surveys.
|
There are no reliable historical by-catches for common skate and the extent of discard is unknown.
|
The stock of common skate remains at a very low level and the trend in the catch rate indicates a negative trend in the stock development, however it is not significant. Based on scientific trawl surveys.
|
Historical landings for halibut show a decrease in catches over the past 10 year period (2007 - 2017) compared to the previous 10 year period (1997 - 2007).
|
The trend in the catch rate of halibut indicates a negative trend in the stock development, however it is not significant. Based on scientific trawl surveys.
|
Over the last 10 years there has been a decrease in fishing mortality for angler, but since a limit value has not yet been established, it is not possible to quantitatively assess whether it is in good condition.
|
There is a significant positive trend in stock development within the last 10 years for angler. Based on scientific trawl surveys.
|
Over the last 10 years, there has been a decline in fishing mortality for common ling, but since a limit value has not yet been established, it is not possible to quantitatively assess whether it is in good condition.
|
There is a significant positive trend in stock development over the past 10 years too long, based on scientific trawl surveys.
|
There are no reliable historical by-catches for starry smooth-hound and the extent of discards is unknown.
|
The trend in the catch rate of starry smooth-hound indicates a positive trend in the stock development, however it is not significant. Based on scientific trawl surveys.
|
There are no reliable historical by-catches for common smooth-hound and the extent of discard is unknown.
|
The trend in the catch rate of common smooth-hound indicates a positive trend in the stock development, however it is not significant. Based on scientific trawl surveys.
|
There are no reliable historical by-catches for greater forkbeard and the extent of discard is unknown.
|
There is a significant positive trend in stock development within the last 10 years for greater forkbeard, based on scientific trawl studies.
|
There are no reliable historical by-catches for thornback ray and the extent of discard is unknown.
|
The trend in the catch rate of thornback ray indicates a positive trend in the stock development, however it is not significant. Based on scientific trawl surveys.
|
There are no reliable historical by-catches for large spotted ray and the extent of discarding is unknown. For the past 3 years, however, between 140 and 300 tonnes have been landed annually in the North Sea.
|
The development in the catch rate of large spotted ray indicates a positive trend in the stock development, however it is not significant. Based on scientific trawl surveys.
|
Historical school shark landings show a decline in catches over the past 10 year period (2007 - 2017) compared to the previous 10 year period (1997 - 2007).
|
The trend in the catch rate of school shark indicates a positive trend in the stock development, however it is not significant. Based on scientific trawl surveys.
|
|
Element status |
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 |
Description element |
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
There is insufficient data to determine absolute stock sizes of non-commercial fish.
|
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
|
Integration rule description parameter |
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
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
|
Integration rule description criteria |
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
No integration rule has been applied
|
GES extent threshold |
||||||||||||||||||||||||||||||
GES extent achieved |
||||||||||||||||||||||||||||||
GES extent unit |
||||||||||||||||||||||||||||||
GES achieved |
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 |
Description overall status |
There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. For coastal fish the condition has been assessed by ICES for flounder and for eelpout a series of time series data compiled by DTU Aqua is used.
|
There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. For coastal fish the condition has been assessed by ICES for flounder and for eelpout a series of time series data compiled by DTU Aqua is used.
|
There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. For coastal fish the condition has been assessed by ICES for flounder and for eelpout a series of time series data compiled by DTU Aqua is used.
|
There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. For coastal fish the condition has been assessed by ICES for flounder and for eelpout a series of time series data compiled by DTU Aqua is used.
|
There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. DTU Aqua has therefore compiled a list of 14 species that are considered to be sensitive to fisheries in Danish marine areas and for which sufficient data is available to assess the temporal development. Since many of the species have not been the subject of major fisheries, there is often no data basis for assessing the absolute population size of the species. Instead, population size trends are indicated by a number index based on data from scientific quests coordinated by ICES.
|
There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. DTU Aqua has therefore compiled a list of 14 species that are considered to be sensitive to fisheries in Danish marine areas and for which sufficient data is available to assess the temporal development. Since many of the species have not been the subject of major fisheries, there is often no data basis for assessing the absolute population size of the species. Instead, population size trends are indicated by a number index based on data from scientific quests coordinated by ICES.
|
There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. DTU Aqua has therefore compiled a list of 14 species that are considered to be sensitive to fisheries in Danish marine areas and for which sufficient data is available to assess the temporal development. Since many of the species have not been the subject of major fisheries, there is often no data basis for assessing the absolute population size of the species. Instead, population size trends are indicated by a number index based on data from scientific quests coordinated by ICES.
|
There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. DTU Aqua has therefore compiled a list of 14 species that are considered to be sensitive to fisheries in Danish marine areas and for which sufficient data is available to assess the temporal development. Since many of the species have not been the subject of major fisheries, there is often no data basis for assessing the absolute population size of the species. Instead, population size trends are indicated by a number index based on data from scientific quests coordinated by ICES.
|
There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. DTU Aqua has therefore compiled a list of 14 species that are considered to be sensitive to fisheries in Danish marine areas and for which sufficient data is available to assess the temporal development. Since many of the species have not been the subject of major fisheries, there is often no data basis for assessing the absolute population size of the species. Instead, population size trends are indicated by a number index based on data from scientific quests coordinated by ICES.
|
There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. DTU Aqua has therefore compiled a list of 14 species that are considered to be sensitive to fisheries in Danish marine areas and for which sufficient data is available to assess the temporal development. Since many of the species have not been the subject of major fisheries, there is often no data basis for assessing the absolute population size of the species. Instead, population size trends are indicated by a number index based on data from scientific quests coordinated by ICES.
|
There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. DTU Aqua has therefore compiled a list of 14 species that are considered to be sensitive to fisheries in Danish marine areas and for which sufficient data is available to assess the temporal development. Since many of the species have not been the subject of major fisheries, there is often no data basis for assessing the absolute population size of the species. Instead, population size trends are indicated by a number index based on data from scientific quests coordinated by ICES.
|
There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. DTU Aqua has therefore compiled a list of 14 species that are considered to be sensitive to fisheries in Danish marine areas and for which sufficient data is available to assess the temporal development. Since many of the species have not been the subject of major fisheries, there is often no data basis for assessing the absolute population size of the species. Instead, population size trends are indicated by a number index based on data from scientific quests coordinated by ICES.
|
There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. DTU Aqua has therefore compiled a list of 14 species that are considered to be sensitive to fisheries in Danish marine areas and for which sufficient data is available to assess the temporal development. Since many of the species have not been the subject of major fisheries, there is often no data basis for assessing the absolute population size of the species. Instead, population size trends are indicated by a number index based on data from scientific quests coordinated by ICES.
|
There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. DTU Aqua has therefore compiled a list of 14 species that are considered to be sensitive to fisheries in Danish marine areas and for which sufficient data is available to assess the temporal development. Since many of the species have not been the subject of major fisheries, there is often no data basis for assessing the absolute population size of the species. Instead, population size trends are indicated by a number index based on data from scientific quests coordinated by ICES.
|
There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. DTU Aqua has therefore compiled a list of 14 species that are considered to be sensitive to fisheries in Danish marine areas and for which sufficient data is available to assess the temporal development. Since many of the species have not been the subject of major fisheries, there is often no data basis for assessing the absolute population size of the species. Instead, population size trends are indicated by a number index based on data from scientific quests coordinated by ICES.
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There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. DTU Aqua has therefore compiled a list of 14 species that are considered to be sensitive to fisheries in Danish marine areas and for which sufficient data is available to assess the temporal development. Since many of the species have not been the subject of major fisheries, there is often no data basis for assessing the absolute population size of the species. Instead, population size trends are indicated by a number index based on data from scientific quests coordinated by ICES.
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There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. DTU Aqua has therefore compiled a list of 14 species that are considered to be sensitive to fisheries in Danish marine areas and for which sufficient data is available to assess the temporal development. Since many of the species have not been the subject of major fisheries, there is often no data basis for assessing the absolute population size of the species. Instead, population size trends are indicated by a number index based on data from scientific quests coordinated by ICES.
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There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. DTU Aqua has therefore compiled a list of 14 species that are considered to be sensitive to fisheries in Danish marine areas and for which sufficient data is available to assess the temporal development. Since many of the species have not been the subject of major fisheries, there is often no data basis for assessing the absolute population size of the species. Instead, population size trends are indicated by a number index based on data from scientific quests coordinated by ICES.
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There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. DTU Aqua has therefore compiled a list of 14 species that are considered to be sensitive to fisheries in Danish marine areas and for which sufficient data is available to assess the temporal development. Since many of the species have not been the subject of major fisheries, there is often no data basis for assessing the absolute population size of the species. Instead, population size trends are indicated by a number index based on data from scientific quests coordinated by ICES.
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There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. DTU Aqua has therefore compiled a list of 14 species that are considered to be sensitive to fisheries in Danish marine areas and for which sufficient data is available to assess the temporal development. Since many of the species have not been the subject of major fisheries, there is often no data basis for assessing the absolute population size of the species. Instead, population size trends are indicated by a number index based on data from scientific quests coordinated by ICES.
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There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. DTU Aqua has therefore compiled a list of 14 species that are considered to be sensitive to fisheries in Danish marine areas and for which sufficient data is available to assess the temporal development. Since many of the species have not been the subject of major fisheries, there is often no data basis for assessing the absolute population size of the species. Instead, population size trends are indicated by a number index based on data from scientific quests coordinated by ICES.
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There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. DTU Aqua has therefore compiled a list of 14 species that are considered to be sensitive to fisheries in Danish marine areas and for which sufficient data is available to assess the temporal development. Since many of the species have not been the subject of major fisheries, there is often no data basis for assessing the absolute population size of the species. Instead, population size trends are indicated by a number index based on data from scientific quests coordinated by ICES.
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There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. DTU Aqua has therefore compiled a list of 14 species that are considered to be sensitive to fisheries in Danish marine areas and for which sufficient data is available to assess the temporal development. Since many of the species have not been the subject of major fisheries, there is often no data basis for assessing the absolute population size of the species. Instead, population size trends are indicated by a number index based on data from scientific quests coordinated by ICES.
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There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. DTU Aqua has therefore compiled a list of 14 species that are considered to be sensitive to fisheries in Danish marine areas and for which sufficient data is available to assess the temporal development. Since many of the species have not been the subject of major fisheries, there is often no data basis for assessing the absolute population size of the species. Instead, population size trends are indicated by a number index based on data from scientific quests coordinated by ICES.
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There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. DTU Aqua has therefore compiled a list of 14 species that are considered to be sensitive to fisheries in Danish marine areas and for which sufficient data is available to assess the temporal development. Since many of the species have not been the subject of major fisheries, there is often no data basis for assessing the absolute population size of the species. Instead, population size trends are indicated by a number index based on data from scientific quests coordinated by ICES.
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There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. DTU Aqua has therefore compiled a list of 14 species that are considered to be sensitive to fisheries in Danish marine areas and for which sufficient data is available to assess the temporal development. Since many of the species have not been the subject of major fisheries, there is often no data basis for assessing the absolute population size of the species. Instead, population size trends are indicated by a number index based on data from scientific quests coordinated by ICES.
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There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. DTU Aqua has therefore compiled a list of 14 species that are considered to be sensitive to fisheries in Danish marine areas and for which sufficient data is available to assess the temporal development. Since many of the species have not been the subject of major fisheries, there is often no data basis for assessing the absolute population size of the species. Instead, population size trends are indicated by a number index based on data from scientific quests coordinated by ICES.
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There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. DTU Aqua has therefore compiled a list of 14 species that are considered to be sensitive to fisheries in Danish marine areas and for which sufficient data is available to assess the temporal development. Since many of the species have not been the subject of major fisheries, there is often no data basis for assessing the absolute population size of the species. Instead, population size trends are indicated by a number index based on data from scientific quests coordinated by ICES.
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There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. DTU Aqua has therefore compiled a list of species that are considered to be sensitive to fisheries in Danish marine areas and for which sufficient data is available to assess the temporal development. Here the gray shark is the only pelagic species included. As many of the species have not been the subject of major fisheries, there is no data basis to assess the absolute population size of the species. Instead, population size trends are indicated by a number index based on data from scientific quests coordinated by ICES.
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There is currently no regionally coordinated list of the by-catch of fish that is not used for commercial purposes. DTU Aqua has therefore compiled a list of species that are considered to be sensitive to fisheries in Danish marine areas and for which sufficient data is available to assess the temporal development. Here the gray shark is the only pelagic species included. As many of the species have not been the subject of major fisheries, there is no data basis to assess the absolute population size of the species. Instead, population size trends are indicated by a number index based on data from scientific quests coordinated by ICES.
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Assessments period |
2008-2015 |
2008-2015 |
2008-2015 |
2008-2015 |
2007-2017 |
2007-2017 |
2007-2017 |
2007-2017 |
2007-2017 |
2007-2017 |
2007-2017 |
2007-2017 |
2007-2017 |
2007-2017 |
2007-2017 |
2007-2017 |
2007-2017 |
2007-2017 |
2007-2017 |
2007-2017 |
2007-2017 |
2007-2017 |
2007-2017 |
2007-2017 |
2007-2017 |
2007-2017 |
2007-2017 |
2007-2017 |
2007-2017 |
2007-2017 |
Related pressures |
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Related targets |
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