Member State report / Art8-2024 / 2024 / D1-M / Ireland / NE Atlantic: Celtic Seas
| Report type | Member State report to Commission |
| MSFD Article | Art8 |
| Report due | 2024-10-15 |
| GES Descriptor | D1 Mammals |
| Member State | Ireland |
| Region/subregion | NE Atlantic: Celtic Seas |
| Report date | 2026-04-09 13:40:20 |
Irish Assesment Area (ACS-IE-AA-001)
Regional assessment area |
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Component MRUs |
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GES component |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
D1M |
Feature |
Baleen whales
|
Baleen whales
|
Baleen whales
|
Baleen whales
|
Baleen whales
|
Baleen whales
|
Baleen whales
|
Baleen whales
|
Baleen whales
|
Baleen whales
|
Deep-diving toothed cetaceans
|
Deep-diving toothed cetaceans
|
Deep-diving toothed cetaceans
|
Deep-diving toothed cetaceans
|
Deep-diving toothed cetaceans
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Small toothed cetaceans
|
Seals
|
Seals
|
Seals
|
Seals
|
Seals
|
Seals
|
Seals
|
Seals
|
Seals
|
Seals
|
Element |
Balaenoptera acutorostrata |
Balaenoptera acutorostrata |
Balaenoptera acutorostrata |
Balaenoptera acutorostrata |
Balaenoptera acutorostrata |
Balaenoptera physalus |
Balaenoptera physalus |
Balaenoptera physalus |
Balaenoptera physalus |
Balaenoptera physalus |
Globicephala melas |
Globicephala melas |
Globicephala melas |
Globicephala melas |
Globicephala melas |
Delphinus delphis |
Delphinus delphis |
Delphinus delphis |
Delphinus delphis |
Delphinus delphis |
Lagenorhynchus acutus |
Lagenorhynchus acutus |
Lagenorhynchus acutus |
Lagenorhynchus acutus |
Lagenorhynchus acutus |
Lagenorhynchus albirostris |
Lagenorhynchus albirostris |
Lagenorhynchus albirostris |
Lagenorhynchus albirostris |
Lagenorhynchus albirostris |
Phocoena phocoena |
Phocoena phocoena |
Phocoena phocoena |
Phocoena phocoena |
Phocoena phocoena |
Tursiops truncatus |
Tursiops truncatus |
Tursiops truncatus |
Tursiops truncatus |
Tursiops truncatus |
Halichoerus grypus |
Halichoerus grypus |
Halichoerus grypus |
Halichoerus grypus |
Halichoerus grypus |
Phoca vitulina |
Phoca vitulina |
Phoca vitulina |
Phoca vitulina |
Phoca vitulina |
Element extent |
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Trend element |
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Element 2 |
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Element source |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
HD |
HD |
HD |
HD |
HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
OSPAR; HD |
Criterion |
D1C1
|
D1C2
|
D1C3
|
D1C4
|
D1C5
|
D1C1
|
D1C2
|
D1C3
|
D1C4
|
D1C5
|
D1C1
|
D1C2
|
D1C3
|
D1C4
|
D1C5
|
D1C1
|
D1C2
|
D1C3
|
D1C4
|
D1C5
|
D1C1
|
D1C2
|
D1C3
|
D1C4
|
D1C5
|
D1C1
|
D1C2
|
D1C3
|
D1C4
|
D1C5
|
D1C1
|
D1C2
|
D1C3
|
D1C4
|
D1C5
|
D1C1
|
D1C2
|
D1C3
|
D1C4
|
D1C5
|
D1C1
|
D1C2
|
D1C3
|
D1C4
|
D1C5
|
D1C1
|
D1C2
|
D1C3
|
D1C4
|
D1C5
|
Parameter |
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Not assessed
|
Distribution (range)
|
Extent
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Not assessed
|
Distribution (range)
|
Extent
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Not assessed
|
Distribution (range)
|
Extent
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Not assessed
|
Distribution (range)
|
Extent
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Not assessed
|
Distribution (range)
|
Extent
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Not assessed
|
Distribution (range)
|
Extent
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Not assessed
|
Distribution (range)
|
Extent
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Not assessed
|
Distribution (range)
|
Extent
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Not assessed
|
Distribution (range)
|
Extent
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Not assessed
|
Distribution (range)
|
Extent
|
Threshold value upper |
-0.5 |
985.0 |
-0.9 |
-0.7 |
-0.7 |
160.0 |
-1.6 |
-0.5 |
3647.0 |
1.0 |
1.0 |
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Threshold value lower |
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Threshold value operator |
<= |
> |
> |
> |
<= |
> |
> |
<= |
> |
> |
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Threshold qualitative |
Sign of trend in abundance estimate. Thresholds, corresponds to average annual rate of decline in abundance that would result in an overall 30% decline if sustained over three generations. |
Species short term range is assessed as stable
|
Species short term habitat is assessed as stable
|
Sign of trend in abundance estimate
|
Species short term range is assessed as stable
|
Species short term habitat is assessed as stable
|
Species short term population is assessed as stable |
Species short term range is assessed as stable
|
Species short term habitat is assessed as stable
|
Sign of trend in abundance estimate. Thresholds, corresponds to average annual rate of decline in abundance that would result in an overall 30% decline if sustained over three generations. |
Species short term range is assessed as stable
|
Species short term habitat is assessed as stable
|
Sign of trend in abundance estimate. Thresholds, corresponds to average annual rate of decline in abundance that would result in an overall 30% decline if sustained over three generations. |
Species short term range is assessed as stable
|
Species short term habitat is assessed as stable
|
Sign of trend in abundance estimate. Thresholds, corresponds to average annual rate of decline in abundance that would result in an overall 30% decline if sustained over three generations. |
Species short term range is assessed as stable
|
Species short term habitat is assessed as stable
|
Sign of trend in abundance estimate. Thresholds, corresponds to average annual rate of decline in abundance that would result in an overall 30% decline if sustained over three generations. |
Species short term range is assessed as stable
|
Species short term habitat is assessed as stable
|
Sign of trend in abundance estimate. Thresholds, corresponds to average annual rate of decline in abundance that would result in an overall 30% decline if sustained over three generations. |
Species short term range is assessed as stable
|
Species short term habitat is assessed as stable
|
No decline in seal abundance of >1% per year in the previous six-year period (this is approximately 6% over 6 years) |
Species short term range is assessed as stable
|
Species short term habitat is assessed as stable
|
No decline in seal abundance of >1% per year in the previous six-year period (this is approximately 6% over 6 years) |
Species short term range is assessed as stable
|
Species short term habitat is assessed as stable
|
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Threshold value source |
OSPAR Convention
|
HD
|
OSPAR Convention
|
HD
|
HD
|
HD
|
HD
|
HD
|
OSPAR Convention
|
OSPAR Convention
|
HD
|
HD
|
OSPAR Convention
|
HD
|
HD
|
OSPAR Convention
|
HD
|
HD
|
OSPAR Convention
|
OSPAR Convention
|
HD
|
HD
|
OSPAR Convention
|
HD
|
HD
|
OSPAR Convention
|
OSPAR Convention
|
HD
|
HD
|
OSPAR Convention
|
HD
|
HD
|
||||||||||||||||||
Value achieved upper |
6406.0 |
1056.0 |
1632.0 |
77.0 |
20.0 |
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Value achieved lower |
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Value unit |
individuals
|
individuals
|
percentage
|
individuals
|
percentage
|
percentage
|
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Proportion threshold value |
100.0 |
100.0 |
100.0 |
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Proportion value achieved |
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Proportion threshold value unit |
% of species achieving threshold value |
% of species achieving threshold value |
% of species achieving threshold value |
% of species achieving threshold value |
% of species achieving threshold value |
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Trend parameter |
Unknown |
Stable |
Not assessed |
Stable |
Unknown |
Unknown |
Not assessed |
Not assessed |
Stable |
Stable |
Unknown |
Unknown |
Not assessed |
Stable |
Stable |
Unknown |
Stable |
Not assessed |
Stable |
Stable |
Unknown |
Not assessed |
Not assessed |
Stable |
Stable |
Unknown |
Stable |
Not assessed |
Stable |
Stable |
Unknown |
Deteriorating |
Not assessed |
Stable |
Stable |
Unknown |
Stable |
Not assessed |
Stable |
Stable |
Unknown |
Stable |
Not assessed |
Stable |
Stable |
Unknown |
Stable |
Not assessed |
Stable |
Stable |
Parameter achieved |
Unknown |
Yes |
Not assessed |
Yes |
Yes |
Unknown |
Not assessed |
Not assessed |
Yes |
Yes |
Unknown |
Yes |
Not assessed |
Yes |
Yes |
No |
Yes |
Not assessed |
Yes |
Yes |
Unknown |
Not assessed |
Not assessed |
Yes |
Yes |
Unknown |
Yes |
Not assessed |
Yes |
Yes |
No |
No |
Not assessed |
Yes |
Yes |
Unknown |
Yes |
Not assessed |
Yes |
Yes |
Yes |
Yes |
Not assessed |
Yes |
Yes |
Unknown |
Yes |
Not assessed |
Yes |
Yes |
Description parameter |
Qualitative assessment based on robust evidence provided by design-based estimates. A quantitative assessment against the threshold was not carried out as no trend was estimated on only two estimates. |
Species short term population is assessed as stable in HD |
Species short term population is assessed as stable in HD |
No assessment because less than 3 abundance estimates |
Species short term population is assessed as stable in HD |
Species short term population is assessed as stable in HD |
Species short term population is assessed as unknown |
Species short term population is assessed as stable in HD |
Species short term habitat is assessed as stable
|
Qualitative assessment based on robust evidence provided by design-based estimates. A quantitative assessment against the threshold was not carried out as
no trend was estimated on only two estimates. |
Species short term population is assessed as stable in HD |
Species short term habitat is assessed as stable
|
No assessment because less than 3 abundance estimates. The abundance
estimate in 2016 is the first estimate available at the scale of the AU. No assessment, qualitative or
quantitative, is possible with a single estimate. |
Species short term population is assessed as stable in HD |
Species short term habitat is assessed as stable
|
A qualitative assessment based on the evidence provided by the design-based estimates is one of no decline in
abundance of striped dolphin in the North-East Atlantic AU. A quantitative assessment against the threshold
was not carried out as there is no defined AU with OSPAR and no trend was estimated on only two estimates. |
Species short term population is assessed as stable in HD |
Species short term habitat is assessed as stable
|
Qualitative assessment based on robust evidence provided by design-based estimates |
Species short term population is assessed as stable in HD |
Species short term habitat is assessed as stable
|
Stable population over the Assessment Period. Qualitative assessment based on robust evidence provided by design-based estimates. A quantitative assessment against the threshold was not carried out as
no trend was estimated on only two estimates. |
Species short term population is assessed as stable in HD |
Species short term habitat is assessed as stable
|
Percentage long-term change. Confidence Intervals (61, 98) |
Species short term population is assessed as stable in HD |
Species short term habitat is assessed as stable
|
Percentage short-term change. Confidence Intervals (14, 29) |
Species short term population is assessed as stable in HD |
Species short term habitat is assessed as stable
|
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Related indicator |
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Criteria status |
Unknown |
Good |
Not assessed |
Good |
Good |
Unknown |
Unknown |
Not assessed |
Good |
Good |
Unknown |
Good |
Not assessed |
Good |
Good |
Not good |
Good |
Not assessed |
Good |
Good |
Unknown |
Unknown |
Not assessed |
Good |
Good |
Unknown |
Good |
Not assessed |
Good |
Good |
Not good |
Not good |
Not assessed |
Good |
Good |
Unknown |
Good |
Not assessed |
Good |
Good |
Good |
Good |
Not assessed |
Good |
Good |
Unknown |
Good |
Not assessed |
Good |
Good |
Description criteria |
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Element status |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Not good |
Not good |
Not good |
Not good |
Not good |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Not good |
Not good |
Not good |
Not good |
Not good |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Good |
Good |
Good |
Good |
Good |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Description element |
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Source assessment feature |
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Reporting method feature |
Type C |
Type C |
Type C |
Type C |
Type C |
Type C |
Type C |
Type C |
Type C |
Type C |
Type C |
Type C |
Type C |
Type C |
Type C |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type C |
Type C |
Type C |
Type C |
Type C |
Type C |
Type C |
Type C |
Type C |
Type C |
Trend feature |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Integration rule type parameter |
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
Integration rule description parameter |
||||||||||||||||||||||||||||||||||||||||||||||||||
Integration rule type criteria |
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
OOAO_HIE
|
Integration rule description criteria |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Baleen whales) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Baleen whales) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Baleen whales) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Baleen whales) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Baleen whales) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Baleen whales) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Baleen whales) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Baleen whales) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Baleen whales) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Baleen whales) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Deep Diving whales) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Deep Diving whales) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Deep Diving whales) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Deep Diving whales) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Deep Diving whales) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Small Toothed cetaceans) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Small Toothed cetaceans) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Small Toothed cetaceans) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Small Toothed cetaceans) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Small Toothed cetaceans) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Small Toothed cetaceans) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Small Toothed cetaceans) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Small Toothed cetaceans) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Small Toothed cetaceans) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Small Toothed cetaceans) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Small Toothed cetaceans) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Small Toothed cetaceans) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Small Toothed cetaceans) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Small Toothed cetaceans) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Small Toothed cetaceans) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Small Toothed cetaceans) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Small Toothed cetaceans) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Small Toothed cetaceans) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Small Toothed cetaceans) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Small Toothed cetaceans) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Small Toothed cetaceans) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Small Toothed cetaceans) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Small Toothed cetaceans) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Small Toothed cetaceans) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Small Toothed cetaceans) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Seals) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Seals) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Seals) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Seals) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Seals) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Seals) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Seals) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Seals) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Seals) to be in GES overall. |
GES is achieved when three of four criteria are in GES and the fourth is unknown or in GES. Mortality due to bycatch must be assessed as being in GES for the feature (Seals) to be in GES overall. |
GES extent threshold |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
GES extent achieved |
||||||||||||||||||||||||||||||||||||||||||||||||||
GES extent unit |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
GES achieved |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES achieved by 2018 |
GES achieved by 2018 |
GES achieved by 2018 |
GES achieved by 2018 |
GES achieved by 2018 |
GES achieved by 2018 |
GES achieved by 2018 |
GES achieved by 2018 |
GES achieved by 2018 |
GES achieved by 2018 |
GES achieved by 2018 |
GES achieved by 2018 |
GES achieved by 2018 |
GES achieved by 2018 |
GES achieved by 2018 |
GES achieved by 2018 |
GES achieved by 2018 |
GES achieved by 2018 |
GES achieved by 2018 |
GES achieved by 2018 |
GES achieved by 2018 |
GES achieved by 2018 |
GES achieved by 2018 |
GES achieved by 2018 |
GES achieved by 2018 |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
Description overall status |
Minke whales and fin whales were assessed under Baleen Whales. As D1C1-mortality was unknown a status could not be given. Both species were in GES for D1C4 and D1C5 and minke whales were also in GES for D1C2. |
Minke whales and fin whales were assessed under Baleen Whales. As D1C1-mortality was unknown a status could not be given. Both species were in GES for D1C4 and D1C5 and minke whales were also in GES for D1C2. |
Minke whales and fin whales were assessed under Baleen Whales. As D1C1-mortality was unknown a status could not be given. Both species were in GES for D1C4 and D1C5 and minke whales were also in GES for D1C2. |
Minke whales and fin whales were assessed under Baleen Whales. As D1C1-mortality was unknown a status could not be given. Both species were in GES for D1C4 and D1C5 and minke whales were also in GES for D1C2. |
Minke whales and fin whales were assessed under Baleen Whales. As D1C1-mortality was unknown a status could not be given. Both species were in GES for D1C4 and D1C5 and minke whales were also in GES for D1C2. |
Minke whales and fin whales were assessed under Baleen Whales. As D1C1-mortality was unknown a status could not be given. Both species were in GES for D1C4 and D1C5 and minke whales were also in GES for D1C2. |
Minke whales and fin whales were assessed under Baleen Whales. As D1C1-mortality was unknown a status could not be given. Both species were in GES for D1C4 and D1C5 and minke whales were also in GES for D1C2. |
Minke whales and fin whales were assessed under Baleen Whales. As D1C1-mortality was unknown a status could not be given. Both species were in GES for D1C4 and D1C5 and minke whales were also in GES for D1C2. |
Minke whales and fin whales were assessed under Baleen Whales. As D1C1-mortality was unknown a status could not be given. Both species were in GES for D1C4 and D1C5 and minke whales were also in GES for D1C2. |
Minke whales and fin whales were assessed under Baleen Whales. As D1C1-mortality was unknown a status could not be given. Both species were in GES for D1C4 and D1C5 and minke whales were also in GES for D1C2. |
One species (long finned pilot whale) was assessed under deep diving whales. D1C2, D1C4 and D1C5 were in GES while D1C1 was unknown. |
One species (long finned pilot whale) was assessed under deep diving whales. D1C2, D1C4 and D1C5 were in GES while D1C1 was unknown. |
One species (long finned pilot whale) was assessed under deep diving whales. D1C2, D1C4 and D1C5 were in GES while D1C1 was unknown. |
One species (long finned pilot whale) was assessed under deep diving whales. D1C2, D1C4 and D1C5 were in GES while D1C1 was unknown. |
One species (long finned pilot whale) was assessed under deep diving whales. D1C2, D1C4 and D1C5 were in GES while D1C1 was unknown. |
Five species were assessed under small toothed cetaceans. Two (harbour porpoise and common dolphin) were not in GES as they did not achieved GES for D1C1. Three others (bottlenose dolphin, white-sided dolphin, white-beaked dolphin) did not achieve GES as D1C1 was unknown. |
Five species were assessed under small toothed cetaceans. Two (harbour porpoise and common dolphin) were not in GES as they did not achieved GES for D1C1. Three others (bottlenose dolphin, white-sided dolphin, white-beaked dolphin) did not achieve GES as D1C1 was unknown. |
Five species were assessed under small toothed cetaceans. Two (harbour porpoise and common dolphin) were not in GES as they did not achieved GES for D1C1. Three others (bottlenose dolphin, white-sided dolphin, white-beaked dolphin) did not achieve GES as D1C1 was unknown. |
Five species were assessed under small toothed cetaceans. Two (harbour porpoise and common dolphin) were not in GES as they did not achieved GES for D1C1. Three others (bottlenose dolphin, white-sided dolphin, white-beaked dolphin) did not achieve GES as D1C1 was unknown. |
Five species were assessed under small toothed cetaceans. Two (harbour porpoise and common dolphin) were not in GES as they did not achieved GES for D1C1. Three others (bottlenose dolphin, white-sided dolphin, white-beaked dolphin) did not achieve GES as D1C1 was unknown. |
Five species were assessed under small toothed cetaceans. Two (harbour porpoise and common dolphin) were not in GES as they did not achieved GES for D1C1. Three others (bottlenose dolphin, white-sided dolphin, white-beaked dolphin) did not achieve GES as D1C1 was unknown. |
Five species were assessed under small toothed cetaceans. Two (harbour porpoise and common dolphin) were not in GES as they did not achieved GES for D1C1. Three others (bottlenose dolphin, white-sided dolphin, white-beaked dolphin) did not achieve GES as D1C1 was unknown. |
Five species were assessed under small toothed cetaceans. Two (harbour porpoise and common dolphin) were not in GES as they did not achieved GES for D1C1. Three others (bottlenose dolphin, white-sided dolphin, white-beaked dolphin) did not achieve GES as D1C1 was unknown. |
Five species were assessed under small toothed cetaceans. Two (harbour porpoise and common dolphin) were not in GES as they did not achieved GES for D1C1. Three others (bottlenose dolphin, white-sided dolphin, white-beaked dolphin) did not achieve GES as D1C1 was unknown. |
Five species were assessed under small toothed cetaceans. Two (harbour porpoise and common dolphin) were not in GES as they did not achieved GES for D1C1. Three others (bottlenose dolphin, white-sided dolphin, white-beaked dolphin) did not achieve GES as D1C1 was unknown. |
Five species were assessed under small toothed cetaceans. Two (harbour porpoise and common dolphin) were not in GES as they did not achieved GES for D1C1. Three others (bottlenose dolphin, white-sided dolphin, white-beaked dolphin) did not achieve GES as D1C1 was unknown. |
Five species were assessed under small toothed cetaceans. Two (harbour porpoise and common dolphin) were not in GES as they did not achieved GES for D1C1. Three others (bottlenose dolphin, white-sided dolphin, white-beaked dolphin) did not achieve GES as D1C1 was unknown. |
Five species were assessed under small toothed cetaceans. Two (harbour porpoise and common dolphin) were not in GES as they did not achieved GES for D1C1. Three others (bottlenose dolphin, white-sided dolphin, white-beaked dolphin) did not achieve GES as D1C1 was unknown. |
Five species were assessed under small toothed cetaceans. Two (harbour porpoise and common dolphin) were not in GES as they did not achieved GES for D1C1. Three others (bottlenose dolphin, white-sided dolphin, white-beaked dolphin) did not achieve GES as D1C1 was unknown. |
Five species were assessed under small toothed cetaceans. Two (harbour porpoise and common dolphin) were not in GES as they did not achieved GES for D1C1. Three others (bottlenose dolphin, white-sided dolphin, white-beaked dolphin) did not achieve GES as D1C1 was unknown. |
Five species were assessed under small toothed cetaceans. Two (harbour porpoise and common dolphin) were not in GES as they did not achieved GES for D1C1. Three others (bottlenose dolphin, white-sided dolphin, white-beaked dolphin) did not achieve GES as D1C1 was unknown. |
Five species were assessed under small toothed cetaceans. Two (harbour porpoise and common dolphin) were not in GES as they did not achieved GES for D1C1. Three others (bottlenose dolphin, white-sided dolphin, white-beaked dolphin) did not achieve GES as D1C1 was unknown. |
Five species were assessed under small toothed cetaceans. Two (harbour porpoise and common dolphin) were not in GES as they did not achieved GES for D1C1. Three others (bottlenose dolphin, white-sided dolphin, white-beaked dolphin) did not achieve GES as D1C1 was unknown. |
Five species were assessed under small toothed cetaceans. Two (harbour porpoise and common dolphin) were not in GES as they did not achieved GES for D1C1. Three others (bottlenose dolphin, white-sided dolphin, white-beaked dolphin) did not achieve GES as D1C1 was unknown. |
Five species were assessed under small toothed cetaceans. Two (harbour porpoise and common dolphin) were not in GES as they did not achieved GES for D1C1. Three others (bottlenose dolphin, white-sided dolphin, white-beaked dolphin) did not achieve GES as D1C1 was unknown. |
Five species were assessed under small toothed cetaceans. Two (harbour porpoise and common dolphin) were not in GES as they did not achieved GES for D1C1. Three others (bottlenose dolphin, white-sided dolphin, white-beaked dolphin) did not achieve GES as D1C1 was unknown. |
Five species were assessed under small toothed cetaceans. Two (harbour porpoise and common dolphin) were not in GES as they did not achieved GES for D1C1. Three others (bottlenose dolphin, white-sided dolphin, white-beaked dolphin) did not achieve GES as D1C1 was unknown. |
Five species were assessed under small toothed cetaceans. Two (harbour porpoise and common dolphin) were not in GES as they did not achieved GES for D1C1. Three others (bottlenose dolphin, white-sided dolphin, white-beaked dolphin) did not achieve GES as D1C1 was unknown. |
Five species were assessed under small toothed cetaceans. Two (harbour porpoise and common dolphin) were not in GES as they did not achieved GES for D1C1. Three others (bottlenose dolphin, white-sided dolphin, white-beaked dolphin) did not achieve GES as D1C1 was unknown. |
Five species were assessed under small toothed cetaceans. Two (harbour porpoise and common dolphin) were not in GES as they did not achieved GES for D1C1. Three others (bottlenose dolphin, white-sided dolphin, white-beaked dolphin) did not achieve GES as D1C1 was unknown. |
Two species were assessed under seals. Grey seals achieved GES. The Harbour seal did not achieved GES as D1C1 was unknown. It did achieve GES for D1C2, D1C4 and D1C5. |
Two species were assessed under seals. Grey seals achieved GES. The Harbour seal did not achieved GES as D1C1 was unknown. It did achieve GES for D1C2, D1C4 and D1C5. |
Two species were assessed under seals. Grey seals achieved GES. The Harbour seal did not achieved GES as D1C1 was unknown. It did achieve GES for D1C2, D1C4 and D1C5. |
Two species were assessed under seals. Grey seals achieved GES. The Harbour seal did not achieved GES as D1C1 was unknown. It did achieve GES for D1C2, D1C4 and D1C5. |
Two species were assessed under seals. Grey seals achieved GES. The Harbour seal did not achieved GES as D1C1 was unknown. It did achieve GES for D1C2, D1C4 and D1C5. |
Two species were assessed under seals. Grey seals achieved GES. The Harbour seal did not achieved GES as D1C1 was unknown. It did achieve GES for D1C2, D1C4 and D1C5. |
Two species were assessed under seals. Grey seals achieved GES. The Harbour seal did not achieved GES as D1C1 was unknown. It did achieve GES for D1C2, D1C4 and D1C5. |
Two species were assessed under seals. Grey seals achieved GES. The Harbour seal did not achieved GES as D1C1 was unknown. It did achieve GES for D1C2, D1C4 and D1C5. |
Two species were assessed under seals. Grey seals achieved GES. The Harbour seal did not achieved GES as D1C1 was unknown. It did achieve GES for D1C2, D1C4 and D1C5. |
Two species were assessed under seals. Grey seals achieved GES. The Harbour seal did not achieved GES as D1C1 was unknown. It did achieve GES for D1C2, D1C4 and D1C5. |
Assessments period |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
Related pressures |
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Related targets |
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Test TV |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
No |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
No |
Yes |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
Yes |
Yes |
NA |
NA |
NA |
NA |
Yes |
NA |
NA |
NA |
Test results |
Correct |
False |
Correct |
False |
False |
Correct |
Correct |
Correct |
False |
False |
Correct |
False |
Correct |
False |
False |
Correct |
False |
Correct |
False |
False |
Correct |
Correct |
Correct |
False |
False |
Correct |
False |
Correct |
False |
False |
Correct |
False |
Correct |
False |
False |
Correct |
False |
Correct |
False |
False |
Correct |
Correct |
Correct |
False |
False |
Correct |
Correct |
Correct |
False |
False |