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.
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.
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 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.
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.
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
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
Related targets
  • DK-T1.11
  • DK-T1.12
  • DKT-1.3
  • DK-T1.11
  • DK-T1.12
  • DKT-1.3
  • DK-T1.11
  • DK-T1.12
  • DKT-1.3
  • DK-T1.11
  • DK-T1.12
  • DKT-1.3
  • DK-T1.11
  • DKT-1.3
  • DK-T1.11
  • DKT-1.3
  • DK-T1.11
  • DKT-1.3
  • DK-T1.11
  • DKT-1.3
  • DK-T1.11
  • DKT-1.3
  • DK-T1.11
  • DKT-1.3
  • DK-T1.11
  • DKT-1.3
  • DK-T1.11
  • DKT-1.3
  • DK-T1.11
  • DKT-1.3
  • DK-T1.11
  • DKT-1.3
  • DK-T1.11
  • DKT-1.3
  • DK-T1.11
  • DKT-1.3
  • DK-T1.11
  • DKT-1.3
  • DK-T1.11
  • DKT-1.3
  • DK-T1.11
  • DKT-1.3
  • DK-T1.11
  • DKT-1.3
  • DK-T1.11
  • DKT-1.3
  • DK-T1.11
  • DKT-1.3
  • DK-T1.11
  • DKT-1.3
  • DK-T1.11
  • DKT-1.3
  • DK-T1.11
  • DKT-1.3
  • DK-T1.11
  • DKT-1.3
  • DK-T1.11
  • DKT-1.3
  • DK-T1.11
  • DKT-1.3
  • DK-T1.11
  • DK-T1.12
  • DK-T1.3
  • DK-T1.11
  • DK-T1.12
  • DK-T1.3