Member State report / Art8-2024 / 2024 / D3 / Estonia / Baltic Sea
| Report type | Member State report to Commission |
| MSFD Article | Art8 |
| Report due | 2024-10-15 |
| GES Descriptor | D3 Commercial fish and shellfish |
| Member State | Estonia |
| Region/subregion | Baltic Sea |
| Report date | 2024-12-11 14:54:57 |
BAL-EE-AA-AA
Regional assessment area |
HELCOML1_SEA000 |
HELCOML1_SEA000 |
HELCOML1_SEA000 |
HELCOML1_SEA000 |
HELCOML1_SEA000 |
HELCOML1_SEA000 |
HELCOML1_SEA000 |
HELCOML1_SEA000 |
HELCOML1_SEA000 |
HELCOML1_SEA000 |
HELCOML1_SEA000 |
HELCOML1_SEA000 |
HELCOML1_SEA000 |
HELCOML1_SEA000 |
HELCOML1_SEA000 |
HELCOML1_SEA000 |
HELCOML1_SEA000 |
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Component MRUs |
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GES component |
D3
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D3
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D3
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D3
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D3
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D3
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D3
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D3
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D3
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D3
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D3
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D3
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D3
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D3
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D3
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D3
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D3
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Feature |
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Element |
Anguilla anguilla |
Anguilla anguilla |
Anguilla anguilla |
Gadus morhua |
Perca fluviatilis |
Salmo salar |
Sprattus sprattus |
Sprattus sprattus |
Sprattus sprattus |
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Element extent |
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Trend element |
Unknown |
Unknown |
Unknown |
Unknown |
Stable |
Stable |
Stable |
Stable |
Stable |
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Element 2 |
European eel (Anguilla anguilla) throughout its natural range |
European eel (Anguilla anguilla) throughout its natural range |
European eel (Anguilla anguilla) throughout its natural range |
Cod (Gadus morhua) in 25-32
|
Sprat (Sprattus sprattus) in subdivisions 22-32 (Baltic Sea) |
Sprat (Sprattus sprattus) in subdivisions 22-32 (Baltic Sea) |
Sprat (Sprattus sprattus) in subdivisions 22-32 (Baltic Sea) |
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Element source |
CFP;EU |
CFP;EU |
CFP;EU |
CFP;EU |
CFP;EU |
CFP;EU |
CFP;EU |
CFP;EU |
CFP;EU |
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Criterion |
D3C1
|
D3C1
|
D3C2
|
D3C2
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D3C2
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D3C2
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D3C2
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D3C3
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D3C1
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D3C2
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D3C3
|
D3C1
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D3C2
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D3C3
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Parameter |
BIOM/Catch ratio
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Mortality rate / Mortality rate from fishing (F)
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Abundance
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ABU-REL
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ABU-REL
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BIOM-SSB
|
BIOM-SSB
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Abundance
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Not assessed
|
ABU-REL
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Not assessed
|
Mortality rate / Mortality rate from fishing (F)
|
BIOM-SSB
|
Not assessed
|
|||
Threshold value upper |
0.6 |
0.34 |
0.6 |
0.6 |
100.0 |
108036.0 |
541000.0 |
0.6 |
100.0 |
0.34 |
541000.0 |
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Threshold value lower |
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Threshold value operator |
>= |
<= |
>= |
>= |
>= |
>= |
>= |
>= |
>= |
<= |
>= |
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Threshold qualitative |
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Threshold value source |
Common Fisheries Policy - Data Collection Framework (DC-MAP)
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Common Fisheries Policy - Data Collection Framework (DC-MAP)
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Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
Common Fisheries Policy - Data Collection Framework (DC-MAP)
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Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
Common Fisheries Policy - Data Collection Framework (DC-MAP)
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Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
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Value achieved upper |
0.25 |
0.36 |
0.48 |
0.23 |
16.0 |
81038.0 |
1050344.0 |
0.38 |
16.0 |
0.355 |
1050344.0 |
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Value achieved lower |
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Value unit |
ratio
|
ratio
|
Catch-Per-Unit-Effort
|
ratio
|
percentage
|
tonne
|
tonne
|
Catch-Per-Unit-Effort
|
percentage
|
ratio
|
tonne
|
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Proportion threshold value |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
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Proportion value achieved |
16.7 |
57.1 |
18.2 |
100.0 |
42.9 |
100.0 |
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Proportion threshold value unit |
% of population achieving threshold value |
% of population achieving threshold value |
% of population achieving threshold value |
% of population achieving threshold value |
% of population achieving threshold value |
% of population achieving threshold value |
% of population achieving threshold value |
% of population achieving threshold value |
% of population achieving threshold value |
% of population achieving threshold value |
% of population achieving threshold value |
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Trend parameter |
Stable |
Stable |
Stable |
Stable |
Unknown |
Unknown |
Stable |
Stable |
Not assessed |
Unknown |
Not assessed |
Stable |
Stable |
Not assessed |
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Parameter achieved |
No |
No |
No |
No |
No |
No |
Yes |
No |
Not assessed |
No |
Not assessed |
No |
Yes |
Not assessed |
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Description parameter |
Ratio between annual commercial catch biomass and biomass index in monitoring fisheries |
The ratio of realized fishing mortality (F) to the fishing mortality that ensures the maximum sustainable yield (MSY) (F/Fmsy) |
Abundance index of sexually mature perch in monitoring catches |
ABU-REL: abundance of spawners compared to salmon spawner abundance estimate PSPC (100%) |
The abundance index of yellow eel recruitment (recruitment index) to the Baltic sea area |
Abundance index of large (TL>250 mm) perch in monitoring catches |
The abundance index of yellow eel recruitment (recruitment index) to the Baltic sea area |
The ratio of realized fishing mortality (F) to the fishing mortality that ensures the maximum sustainable yield (MSY) (F/Fmsy) |
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Related indicator |
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Criteria status |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not assessed |
Not good |
Not assessed |
Not good |
Good |
Not assessed |
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Description criteria |
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Element status |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
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Description element |
assessment based on ICES (2022) assessment: Joint EIFAAC/ICES/GFCM Working Group on Eels (WGEEL). ICES Scientific Reports. 4:62. 297 pp. http://doi.org/10.17895/ices.pub.20418840 |
assessment based on ICES (2022) assessment: Joint EIFAAC/ICES/GFCM Working Group on Eels (WGEEL). ICES Scientific Reports. 4:62. 297 pp. http://doi.org/10.17895/ices.pub.20418840 |
assessment based on ICES (2022) assessment: Joint EIFAAC/ICES/GFCM Working Group on Eels (WGEEL). ICES Scientific Reports. 4:62. 297 pp. http://doi.org/10.17895/ices.pub.20418840 |
assessment based on ICES (2022) assessment: Baltic Fisheries Assessment Working Group (WGBFAS). ICES Scientific Reports. 4:44. 659 pp. http://doi.org/10.17895/ices.pub.19793014 |
assessment based on D3C1 and D3C2; D3C3 not assessed |
assessment based on D3C1 and D3C2; D3C3 not assessed |
assessment based on D3C1 and D3C2; D3C3 not assessed |
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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 C |
Type C |
Trend feature |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Integration rule type parameter |
Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Integration rule description parameter |
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Integration rule type criteria |
OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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OOAO
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Integration rule description criteria |
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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 |
GES extent achieved |
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GES extent unit |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
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 later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
Description overall status |
The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data. |
The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data. |
The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data. |
The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data. |
The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data. |
The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data. |
The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data. |
The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data. |
The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data. |
The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data. |
The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data. |
The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data. |
The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data. |
The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data. |
The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data. |
The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data. |
The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data. |
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 |
Related pressures |
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Related targets |
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Test TV |
No |
No |
No |
No |
No |
No |
Yes |
No |
NA |
No |
NA |
NA |
NA |
NA |
No |
Yes |
NA |
Test results |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
False |
False |
Correct |
Correct |
Correct |
BAL-EE-AA-EE_13
Regional assessment area |
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|---|---|---|---|---|
Component MRUs |
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GES component |
D3
|
D3
|
D3
|
D3
|
Feature |
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Element |
Sander lucioperca |
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Element extent |
||||
Trend element |
Stable |
|||
Element 2 |
||||
Element source |
CFP;EU |
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Criterion |
D3C1
|
D3C2
|
D3C3
|
|
Parameter |
BIOM/Catch ratio
|
Abundance
|
LBI
|
|
Threshold value upper |
0.6 |
0.6 |
0.6 |
|
Threshold value lower |
||||
Threshold value operator |
>= |
>= |
>= |
|
Threshold qualitative |
||||
Threshold value source |
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
|
Value achieved upper |
0.38 |
0.38 |
0.38 |
|
Value achieved lower |
||||
Value unit |
ratio
|
Catch-Per-Unit-Effort
|
ratio
|
|
Proportion threshold value |
100.0 |
100.0 |
100.0 |
|
Proportion value achieved |
||||
Proportion threshold value unit |
% of population achieving threshold value |
% of population achieving threshold value |
% of population achieving threshold value |
|
Trend parameter |
Stable |
Stable |
Stable |
|
Parameter achieved |
No |
No |
No |
|
Description parameter |
Ratio between annual commercial catch biomass and biomass index in monitoring fisheries |
Abundance index of sexually mature female pikeperch |
Aggregated value for 95 % percentile of the length distribution of pikeperch in monitoring catches |
|
Related indicator |
||||
Criteria status |
Not good |
Not good |
Not good |
|
Description criteria |
||||
Element status |
Not good |
|||
Description element |
||||
Source assessment feature |
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|
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Reporting method feature |
Type D |
Type D |
Type D |
Type D |
Trend feature |
Stable |
Stable |
Stable |
Stable |
Integration rule type parameter |
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description parameter |
||||
Integration rule type criteria |
OOAO
|
OOAO
|
OOAO
|
OOAO
|
Integration rule description criteria |
||||
GES extent threshold |
100.00 |
100.00 |
100.00 |
100.00 |
GES extent achieved |
||||
GES extent unit |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
GES achieved |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
GES later than 2024, Art14ExceptionNotReported |
Description overall status |
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Assessments period |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
Related pressures |
|
|
|
|
Related targets |
|
|
|
|
Test TV |
No |
No |
No |
NA |
Test results |
Correct |
Correct |
Correct |
False |
BAL-EE-AA-EGB-Coastal
Regional assessment area |
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|---|---|---|---|---|---|---|
Component MRUs |
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GES component |
D3
|
D3
|
D3
|
D3
|
D3
|
D3
|
Feature |
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Element |
Platichthys flesus |
Platichthys flesus |
Platichthys flesus |
|||
Element extent |
||||||
Trend element |
Stable |
Stable |
Stable |
|||
Element 2 |
Flounder (Platichthys flesus) in Subdivisions 27 and 29-32 (northern central and northern Baltic Sea) |
Flounder (Platichthys flesus) in Subdivisions 27 and 29-32 (northern central and northern Baltic Sea) |
Flounder (Platichthys flesus) in Subdivisions 27 and 29-32 (northern central and northern Baltic Sea) |
|||
Element source |
CFP;EU |
CFP;EU |
CFP;EU |
|||
Criterion |
D3C1
|
D3C2
|
D3C3
|
D3C1
|
D3C2
|
D3C3
|
Parameter |
BIOM/Catch ratio
|
Abundance
|
LBI
|
BIOM/Catch ratio
|
Abundance
|
LBI
|
Threshold value upper |
0.6 |
0.6 |
0.6 |
0.6 |
0.6 |
0.6 |
Threshold value lower |
||||||
Threshold value operator |
>= |
>= |
>= |
>= |
>= |
>= |
Threshold qualitative |
||||||
Threshold value source |
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
Value achieved upper |
0.63 |
0.63 |
0.38 |
0.625 |
0.625 |
0.375 |
Value achieved lower |
||||||
Value unit |
ratio
|
Catch-Per-Unit-Effort
|
ratio
|
ratio
|
Catch-Per-Unit-Effort
|
ratio
|
Proportion threshold value |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
100.0 |
Proportion value achieved |
100.0 |
100.0 |
100.0 |
100.0 |
||
Proportion threshold value unit |
% of population achieving threshold value |
% of population achieving threshold value |
% of population achieving threshold value |
% of population achieving threshold value |
% of population achieving threshold value |
% of population achieving threshold value |
Trend parameter |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Parameter achieved |
Yes |
Yes |
No |
Yes |
Yes |
No |
Description parameter |
Ratio between annual commercial catch biomass and biomass index in monitoring fisheries |
Abundance index of sexually mature flounders is used for assessment |
Aggregated value for 95 % percentile of the length distribution of flounders in monitoring catches |
Ratio between annual commercial catch biomass and biomass index in monitoring fisheries |
Abundance index of sexually mature flounders is used for assessment |
Aggregated value for 95 % percentile of the length distribution of flounders in monitoring catches |
Related indicator |
||||||
Criteria status |
Good |
Good |
Not good |
Good |
Good |
Not good |
Description criteria |
||||||
Element status |
Not good |
Not good |
Not good |
|||
Description element |
||||||
Source assessment feature |
|
|
|
|
|
|
Reporting method feature |
Type C |
Type C |
Type C |
Type C |
Type C |
Type C |
Trend feature |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Integration rule type parameter |
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description parameter |
||||||
Integration rule type criteria |
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
Integration rule description criteria |
||||||
GES extent threshold |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
GES extent achieved |
||||||
GES extent unit |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
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 |
Description overall status |
||||||
Assessments period |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
Related pressures |
|
|
|
|
|
|
Related targets |
|
|
|
|
|
|
Test TV |
Yes |
Yes |
No |
Yes |
Yes |
No |
Test results |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
BAL-EE-AA-ICES_28-1
Regional assessment area |
|||||
|---|---|---|---|---|---|
Component MRUs |
|||||
GES component |
D3
|
D3
|
D3
|
D3
|
D3
|
Feature |
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Element |
Clupea harengus |
Clupea harengus |
Clupea harengus |
||
Element extent |
|||||
Trend element |
Stable |
Stable |
Stable |
||
Element 2 |
Baltic Herring (Clupea harengus membras) in Subdivision 28.1 |
Baltic Herring (Clupea harengus membras) in Subdivision 28.1 |
Baltic Herring (Clupea harengus membras) in Subdivision 28.1 |
||
Element source |
CFP;EU |
CFP;EU |
CFP;EU |
||
Criterion |
D3C1
|
D3C2
|
D3C1
|
D3C2
|
D3C3
|
Parameter |
Mortality rate / Mortality rate from fishing (F)
|
BIOM-SSB
|
Mortality rate / Mortality rate from fishing (F)
|
BIOM-SSB
|
Not assessed
|
Threshold value upper |
0.28 |
72907.0 |
0.28 |
72907.0 |
|
Threshold value lower |
|||||
Threshold value operator |
<= |
>= |
<= |
>= |
|
Threshold qualitative |
|||||
Threshold value source |
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
|
Value achieved upper |
0.27 |
110763.0 |
0.267 |
110763.0 |
|
Value achieved lower |
|||||
Value unit |
ratio
|
tonne
|
ratio
|
tonne
|
|
Proportion threshold value |
100.0 |
100.0 |
100.0 |
100.0 |
|
Proportion value achieved |
100.0 |
100.0 |
100.0 |
100.0 |
|
Proportion threshold value unit |
% of population achieving threshold value |
% of population achieving threshold value |
% of population achieving threshold value |
% of population achieving threshold value |
|
Trend parameter |
Improving |
Stable |
Improving |
Stable |
Not assessed |
Parameter achieved |
Yes |
Yes |
Yes |
Yes |
Not assessed |
Description parameter |
The ratio of realized fishing mortality (F) to the fishing mortality that ensures the maximum sustainable yield (MSY) (F/Fmsy) |
The ratio of realized fishing mortality (F) to the fishing mortality that ensures the maximum sustainable yield (MSY) (F/Fmsy) |
|||
Related indicator |
|||||
Criteria status |
Good |
Good |
Good |
Good |
Not assessed |
Description criteria |
|||||
Element status |
Good |
Good |
Good |
||
Description element |
assessment based on D3C1 and D3C2; D3C3 not assessed |
assessment based on D3C1 and D3C2; D3C3 not assessed |
assessment based on D3C1 and D3C2; D3C3 not assessed |
||
Source assessment feature |
|
|
|
|
|
Reporting method feature |
Type B2 |
Type B2 |
Type B2 |
Type B2 |
Type B2 |
Trend feature |
Stable |
Stable |
Stable |
Stable |
Stable |
Integration rule type parameter |
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description parameter |
|||||
Integration rule type criteria |
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
Integration rule description criteria |
|||||
GES extent threshold |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
GES extent achieved |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
GES extent unit |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
GES achieved |
GES achieved by 2024 |
GES achieved by 2024 |
GES achieved by 2024 |
GES achieved by 2024 |
GES achieved by 2024 |
Description overall status |
The criterion D3C3 was not assessed for Clupea harengus membras because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. |
The criterion D3C3 was not assessed for Clupea harengus membras because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. |
The criterion D3C3 was not assessed for Clupea harengus membras because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. |
The criterion D3C3 was not assessed for Clupea harengus membras because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. |
The criterion D3C3 was not assessed for Clupea harengus membras because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. |
Assessments period |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
Related pressures |
|
|
|
|
|
Related targets |
|
|
|
|
|
Test TV |
Yes |
Yes |
Yes |
Yes |
NA |
Test results |
Correct |
Correct |
Correct |
Correct |
Correct |
BAL-EE-AA-ICES_28-2
Regional assessment area |
|||||
|---|---|---|---|---|---|
Component MRUs |
|||||
GES component |
D3
|
D3
|
D3
|
D3
|
D3
|
Feature |
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Element |
Clupea harengus |
Clupea harengus |
Clupea harengus |
||
Element extent |
|||||
Trend element |
Deteriorating |
Deteriorating |
Deteriorating |
||
Element 2 |
Baltic Herring (Clupea harengus membras) in Subdivision 25–27, 28.2, 29 & 32 |
Baltic Herring (Clupea harengus membras) in Subdivision 25–27, 28.2, 29 & 32 |
Baltic Herring (Clupea harengus membras) in Subdivision 25–27, 28.2, 29 & 32 |
||
Element source |
CFP;EU |
CFP;EU |
CFP;EU |
||
Criterion |
D3C1
|
D3C2
|
D3C1
|
D3C2
|
D3C3
|
Parameter |
Mortality rate / Mortality rate from fishing (F)
|
BIOM-SSB
|
Mortality rate / Mortality rate from fishing (F)
|
BIOM-SSB
|
Not assessed
|
Threshold value upper |
1.0 |
1.0 |
1.0 |
1.0 |
|
Threshold value lower |
|||||
Threshold value operator |
<= |
>= |
<= |
>= |
|
Threshold qualitative |
|||||
Threshold value source |
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
|
Value achieved upper |
1.76 |
0.52 |
1.76 |
0.515 |
|
Value achieved lower |
|||||
Value unit |
ratio
|
ratio
|
ratio
|
ratio
|
|
Proportion threshold value |
100.0 |
100.0 |
100.0 |
100.0 |
|
Proportion value achieved |
|||||
Proportion threshold value unit |
% of population achieving threshold value |
% of population achieving threshold value |
% of population achieving threshold value |
% of population achieving threshold value |
|
Trend parameter |
Deteriorating |
Deteriorating |
Deteriorating |
Deteriorating |
Not assessed |
Parameter achieved |
No |
No |
No |
No |
Not assessed |
Description parameter |
The ratio of realized fishing mortality (F) to the fishing mortality that ensures the maximum sustainable yield (MSY) (F/Fmsy) |
The SSB/MSYBtrigger ratio was used for the assessment of spawning stock biomass (SSB): the ratio of the estimated spawning stock biomass (SSB) to the minimum spawning biomass (MSYBtrigger), which ensures maximum sustainable yield when fishing mortality Fmsy is applied. |
The ratio of realized fishing mortality (F) to the fishing mortality that ensures the maximum sustainable yield (MSY) (F/Fmsy) |
The SSB/MSYBtrigger ratio was used for the assessment of spawning stock biomass (SSB): the ratio of the estimated spawning stock biomass (SSB) to the minimum spawning biomass (MSYBtrigger), which ensures maximum sustainable yield when fishing mortality Fmsy is applied. |
|
Related indicator |
|||||
Criteria status |
Not good |
Not good |
Not good |
Not good |
Not assessed |
Description criteria |
|||||
Element status |
Not good |
Not good |
Not good |
||
Description element |
assessment based on D3C1 and D3C2; D3C3 not assessed |
assessment based on D3C1 and D3C2; D3C3 not assessed |
assessment based on D3C1 and D3C2; D3C3 not assessed |
||
Source assessment feature |
|
|
|
|
|
Reporting method feature |
Type B2 |
Type B2 |
Type B2 |
Type B2 |
Type B2 |
Trend feature |
Deteriorating |
Deteriorating |
Deteriorating |
Deteriorating |
Deteriorating |
Integration rule type parameter |
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description parameter |
|||||
Integration rule type criteria |
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
Integration rule description criteria |
|||||
GES extent threshold |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
GES extent achieved |
|||||
GES extent unit |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
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 |
Description overall status |
The criterion D3C3 was not assessed for Clupea harengus membras because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. |
The criterion D3C3 was not assessed for Clupea harengus membras because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. |
The criterion D3C3 was not assessed for Clupea harengus membras because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. |
The criterion D3C3 was not assessed for Clupea harengus membras because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. |
The criterion D3C3 was not assessed for Clupea harengus membras because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. |
Assessments period |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
Related pressures |
|
|
|
|
|
Related targets |
|
|
|
|
|
Test TV |
No |
No |
No |
No |
NA |
Test results |
Correct |
Correct |
Correct |
Correct |
Correct |
BAL-EE-AA-ICES_29
Regional assessment area |
|||||
|---|---|---|---|---|---|
Component MRUs |
|||||
GES component |
D3
|
D3
|
D3
|
D3
|
D3
|
Feature |
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Element |
Clupea harengus |
Clupea harengus |
Clupea harengus |
||
Element extent |
|||||
Trend element |
Deteriorating |
Deteriorating |
Deteriorating |
||
Element 2 |
Baltic Herring (Clupea harengus membras) in Subdivision 25–27, 28.2, 29 & 32 |
Baltic Herring (Clupea harengus membras) in Subdivision 25–27, 28.2, 29 & 32 |
Baltic Herring (Clupea harengus membras) in Subdivision 25–27, 28.2, 29 & 32 |
||
Element source |
CFP;EU |
CFP;EU |
CFP;EU |
||
Criterion |
D3C1
|
D3C2
|
D3C1
|
D3C2
|
D3C3
|
Parameter |
Mortality rate / Mortality rate from fishing (F)
|
BIOM-SSB
|
Mortality rate / Mortality rate from fishing (F)
|
BIOM-SSB
|
Not assessed
|
Threshold value upper |
1.0 |
1.0 |
1.0 |
1.0 |
|
Threshold value lower |
|||||
Threshold value operator |
<= |
>= |
<= |
>= |
|
Threshold qualitative |
|||||
Threshold value source |
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
|
Value achieved upper |
1.76 |
0.52 |
1.76 |
0.515 |
|
Value achieved lower |
|||||
Value unit |
ratio
|
ratio
|
ratio
|
ratio
|
|
Proportion threshold value |
100.0 |
100.0 |
100.0 |
100.0 |
|
Proportion value achieved |
|||||
Proportion threshold value unit |
% of population achieving threshold value |
% of population achieving threshold value |
% of population achieving threshold value |
% of population achieving threshold value |
|
Trend parameter |
Deteriorating |
Deteriorating |
Deteriorating |
Deteriorating |
Not assessed |
Parameter achieved |
No |
No |
No |
No |
Not assessed |
Description parameter |
The ratio of realized fishing mortality (F) to the fishing mortality that ensures the maximum sustainable yield (MSY) (F/Fmsy) |
The SSB/MSYBtrigger ratio was used for the assessment of spawning stock biomass (SSB): the ratio of the estimated spawning stock biomass (SSB) to the minimum spawning biomass (MSYBtrigger), which ensures maximum sustainable yield when fishing mortality Fmsy is applied. |
The ratio of realized fishing mortality (F) to the fishing mortality that ensures the maximum sustainable yield (MSY) (F/Fmsy) |
The SSB/MSYBtrigger ratio was used for the assessment of spawning stock biomass (SSB): the ratio of the estimated spawning stock biomass (SSB) to the minimum spawning biomass (MSYBtrigger), which ensures maximum sustainable yield when fishing mortality Fmsy is applied. |
|
Related indicator |
|||||
Criteria status |
Not good |
Not good |
Not good |
Not good |
Not assessed |
Description criteria |
|||||
Element status |
Not good |
Not good |
Not good |
||
Description element |
assessment based on D3C1 and D3C2; D3C3 not assessed |
assessment based on D3C1 and D3C2; D3C3 not assessed |
assessment based on D3C1 and D3C2; D3C3 not assessed |
||
Source assessment feature |
|
|
|
|
|
Reporting method feature |
Type B2 |
Type B2 |
Type B2 |
Type B2 |
Type B2 |
Trend feature |
Deteriorating |
Deteriorating |
Deteriorating |
Deteriorating |
Deteriorating |
Integration rule type parameter |
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description parameter |
|||||
Integration rule type criteria |
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
Integration rule description criteria |
|||||
GES extent threshold |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
GES extent achieved |
|||||
GES extent unit |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
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 |
Description overall status |
The criterion D3C3 was not assessed for Clupea harengus membras because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. |
The criterion D3C3 was not assessed for Clupea harengus membras because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. |
The criterion D3C3 was not assessed for Clupea harengus membras because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. |
The criterion D3C3 was not assessed for Clupea harengus membras because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. |
The criterion D3C3 was not assessed for Clupea harengus membras because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. |
Assessments period |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
Related pressures |
|
|
|
|
|
Related targets |
|
|
|
|
|
Test TV |
No |
No |
No |
No |
NA |
Test results |
Correct |
Correct |
Correct |
Correct |
Correct |
BAL-EE-AA-ICES_32
Regional assessment area |
|||||
|---|---|---|---|---|---|
Component MRUs |
|||||
GES component |
D3
|
D3
|
D3
|
D3
|
D3
|
Feature |
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Element |
Clupea harengus |
Clupea harengus |
Clupea harengus |
||
Element extent |
|||||
Trend element |
Deteriorating |
Deteriorating |
Deteriorating |
||
Element 2 |
Baltic Herring (Clupea harengus membras) in Subdivision 25–27, 28.2, 29 & 32 |
Baltic Herring (Clupea harengus membras) in Subdivision 25–27, 28.2, 29 & 32 |
Baltic Herring (Clupea harengus membras) in Subdivision 25–27, 28.2, 29 & 32 |
||
Element source |
CFP;EU |
CFP;EU |
CFP;EU |
||
Criterion |
D3C1
|
D3C2
|
D3C1
|
D3C2
|
D3C3
|
Parameter |
Mortality rate / Mortality rate from fishing (F)
|
BIOM-SSB
|
Mortality rate / Mortality rate from fishing (F)
|
BIOM-SSB
|
Not assessed
|
Threshold value upper |
1.0 |
1.0 |
1.0 |
1.0 |
|
Threshold value lower |
|||||
Threshold value operator |
<= |
>= |
<= |
>= |
|
Threshold qualitative |
|||||
Threshold value source |
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
Common Fisheries Policy - Data Collection Framework (DC-MAP)
|
|
Value achieved upper |
1.76 |
0.52 |
1.76 |
0.515 |
|
Value achieved lower |
|||||
Value unit |
ratio
|
ratio
|
ratio
|
ratio
|
|
Proportion threshold value |
100.0 |
100.0 |
100.0 |
100.0 |
|
Proportion value achieved |
|||||
Proportion threshold value unit |
% of population achieving threshold value |
% of population achieving threshold value |
% of population achieving threshold value |
% of population achieving threshold value |
|
Trend parameter |
Deteriorating |
Deteriorating |
Deteriorating |
Deteriorating |
Not assessed |
Parameter achieved |
No |
No |
No |
No |
Not assessed |
Description parameter |
The ratio of realized fishing mortality (F) to the fishing mortality that ensures the maximum sustainable yield (MSY) (F/Fmsy) |
The SSB/MSYBtrigger ratio was used for the assessment of spawning stock biomass (SSB): the ratio of the estimated spawning stock biomass (SSB) to the minimum spawning biomass (MSYBtrigger), which ensures maximum sustainable yield when fishing mortality Fmsy is applied. |
The ratio of realized fishing mortality (F) to the fishing mortality that ensures the maximum sustainable yield (MSY) (F/Fmsy) |
The SSB/MSYBtrigger ratio was used for the assessment of spawning stock biomass (SSB): the ratio of the estimated spawning stock biomass (SSB) to the minimum spawning biomass (MSYBtrigger), which ensures maximum sustainable yield when fishing mortality Fmsy is applied. |
|
Related indicator |
|||||
Criteria status |
Not good |
Not good |
Not good |
Not good |
Not assessed |
Description criteria |
|||||
Element status |
Not good |
Not good |
Not good |
||
Description element |
assessment based on D3C1 and D3C2; D3C3 not assessed |
assessment based on D3C1 and D3C2; D3C3 not assessed |
assessment based on D3C1 and D3C2; D3C3 not assessed |
||
Source assessment feature |
|
|
|
|
|
Reporting method feature |
Type B2 |
Type B2 |
Type B2 |
Type B2 |
Type B2 |
Trend feature |
Deteriorating |
Deteriorating |
Deteriorating |
Deteriorating |
Deteriorating |
Integration rule type parameter |
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description parameter |
|||||
Integration rule type criteria |
OOAO
|
OOAO
|
OOAO
|
OOAO
|
OOAO
|
Integration rule description criteria |
|||||
GES extent threshold |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
GES extent achieved |
|||||
GES extent unit |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
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 |
Description overall status |
The criterion D3C3 was not assessed for Clupea harengus membras because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. |
The criterion D3C3 was not assessed for Clupea harengus membras because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. |
The criterion D3C3 was not assessed for Clupea harengus membras because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. |
The criterion D3C3 was not assessed for Clupea harengus membras because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. |
The criterion D3C3 was not assessed for Clupea harengus membras because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. |
Assessments period |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
2016-2021 |
Related pressures |
|
|
|
|
|
Related targets |
|
|
|
|
|
Test TV |
No |
No |
No |
No |
NA |
Test results |
Correct |
Correct |
Correct |
Correct |
Correct |