Art8-2024

Member State report / Art8-2024 / 2024 / D3 / Germany / 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	Germany
Region/subregion	Baltic Sea
Report date	2024-10-15 10:22:35

BAL-DE-MS-001

Simplified table

Regional assessment area
Component MRUs
GES component	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	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	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	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	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	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	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	Abramis brama	Abramis brama	Abramis brama	Ammodytes spp.	Ammodytes spp.	Ammodytes spp.	Anguilla anguilla	Anguilla anguilla	Anguilla anguilla	Belone belone	Belone belone	Belone belone	Clupea harengus	Clupea harengus	Clupea harengus	Clupea harengus	Esox lucius	Esox lucius	Esox lucius	Gadus morhua	Gadus morhua	Gadus morhua	Gadus morhua	Gadus morhua	Gadus morhua	Gadus morhua	Gadus morhua	Limanda limanda	Limanda limanda	Limanda limanda	Merlangius merlangus	Merlangius merlangus	Merlangius merlangus	Mytilus edulis	Mytilus edulis	Mytilus edulis	Palaemon elegans	Palaemon elegans	Palaemon elegans	Perca fluviatilis	Perca fluviatilis	Perca fluviatilis	Platichthys flesus	Platichthys flesus	Platichthys flesus	Platichthys solemdali	Platichthys solemdali	Platichthys solemdali	Pleuronectes platessa	Pleuronectes platessa	Pleuronectes platessa	Pleuronectes platessa	Pleuronectes platessa	Pleuronectes platessa	Pleuronectes platessa	Rutilus rutilus	Rutilus rutilus	Rutilus rutilus	Salmo salar	Salmo salar	Salmo salar	Salmo trutta trutta	Salmo trutta trutta	Salmo trutta trutta	Sander lucioperca	Sander lucioperca	Sander lucioperca	Scophthalmus maximus	Scophthalmus maximus	Scophthalmus maximus	Scophthalmus rhombus	Scophthalmus rhombus	Scophthalmus rhombus	Solea solea (sin. vulgaris)	Solea solea (sin. vulgaris)	Solea solea (sin. vulgaris)	Solea solea (sin. vulgaris)	Sprattus sprattus	Sprattus sprattus	Sprattus sprattus	Sprattus sprattus
Element extent
Trend element	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Stable	Stable	Stable	Unknown	Unknown	Unknown	Stable	Stable	Stable	Stable	Unknown	Unknown	Unknown	Stable	Stable	Stable	Stable	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Stable	Stable	Stable	Stable	Improving	Improving	Improving	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable
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				Herring (Clupea harengus) in Subdivisions 20-24, spring spawners (Skagerrak, Kattegat, and western Baltic)	Herring (Clupea harengus) in Subdivisions 20-24, spring spawners (Skagerrak, Kattegat, and western Baltic)	Herring (Clupea harengus) in Subdivisions 20-24, spring spawners (Skagerrak, Kattegat, and western Baltic)	Herring (Clupea harengus) in Subdivisions 20-24, spring spawners (Skagerrak, Kattegat, and western Baltic)				Cod (Gadus morhua) in Subdivisions 22-24, western Baltic stock (western Baltic Sea)	Cod (Gadus morhua) in Subdivisions 22-24, western Baltic stock (western Baltic Sea)	Cod (Gadus morhua) in Subdivisions 22-24, western Baltic stock (western Baltic Sea)	Cod (Gadus morhua) in Subdivisions 22-24, western Baltic stock (western Baltic Sea)	Cod (Gadus morhua) in Subdivisions 24-32, eastern Baltic stock (eastern Baltic Sea)	Cod (Gadus morhua) in Subdivisions 24-32, eastern Baltic stock (eastern Baltic Sea)	Cod (Gadus morhua) in Subdivisions 24-32, eastern Baltic stock (eastern Baltic Sea)	Cod (Gadus morhua) in Subdivisions 24-32, eastern Baltic stock (eastern Baltic Sea)	Dab (Limanda limanda) in subdivisions 22-32 (Baltic Sea)	Dab (Limanda limanda) in subdivisions 22-32 (Baltic Sea)	Dab (Limanda limanda) in subdivisions 22-32 (Baltic Sea)													Flounder (Platichthys flesus) in Subdivisions 22 and 23 (Belts and Sound)	Flounder (Platichthys flesus) in Subdivisions 22 and 23 (Belts and Sound)	Flounder (Platichthys flesus) in Subdivisions 22 and 23 (Belts and Sound)				Plaice (Pleuronectes platessa) in 21-23	Plaice (Pleuronectes platessa) in 21-23	Plaice (Pleuronectes platessa) in 21-23	Plaice (Pleuronectes platessa) in 21-23	Plaice (Pleuronectes platessa) in subdivisions 24-32 (Baltic Sea, excluding the Sound and Belt Seas)	Plaice (Pleuronectes platessa) in subdivisions 24-32 (Baltic Sea, excluding the Sound and Belt Seas)	Plaice (Pleuronectes platessa) in subdivisions 24-32 (Baltic Sea, excluding the Sound and Belt Seas)				Salmon (Salmo salar) in subdivisions 22-31 (Baltic Sea, excluding the Gulf of Finland)	Salmon (Salmo salar) in subdivisions 22-31 (Baltic Sea, excluding the Gulf of Finland)	Salmon (Salmo salar) in subdivisions 22-31 (Baltic Sea, excluding the Gulf of Finland)							Turbot (Scophthalmus maximus) in subdivisions 22–32 (Baltic Sea)	Turbot (Scophthalmus maximus) in subdivisions 22–32 (Baltic Sea)	Turbot (Scophthalmus maximus) in subdivisions 22–32 (Baltic Sea)				Sole (Solea solea) in Subdivisions 20 and 24 (Skagerrak and Kattegat, western Baltic Sea)	Sole (Solea solea) in Subdivisions 20 and 24 (Skagerrak and Kattegat, western Baltic Sea)	Sole (Solea solea) in Subdivisions 20 and 24 (Skagerrak and Kattegat, western Baltic Sea)	Sole (Solea solea) in Subdivisions 20 and 24 (Skagerrak and Kattegat, western Baltic Sea)	Sprat (Sprattus sprattus balticus) in subdivisions 22–32	Sprat (Sprattus sprattus balticus) in subdivisions 22–32	Sprat (Sprattus sprattus balticus) in subdivisions 22–32	Sprat (Sprattus sprattus balticus) in subdivisions 22–32
Element source	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National
Criterion	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C3	D3C1	D3C2	D3C3	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C3	D3C1	D3C2	D3C3	D3C3
Parameter	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	BIOM-SSB	Unknown	Unknown	Unknown	Unknown	Mortality rate / Mortality rate from fishing (F)	BIOM-SSB	R	Ratio SSB/R	Unknown	Unknown	Unknown	Mortality rate / Mortality rate from fishing (F)	BIOM-SSB	R	Ratio SSB/R	Mortality rate / Mortality rate from fishing (F)	BIOM-SSB	R	Ratio SSB/R	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Mortality rate / Mortality rate from fishing (F)	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Mortality rate / Mortality rate from fishing (F)	BIOM-SSB-relative	Unknown		BIOM-SSB-relative	Unknown	Mortality rate / Mortality rate from fishing (F)	BIOM-SSB	R	Ratio SSB/R	Mortality rate / Mortality rate from fishing (F)	BIOM-SSB-relative	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	BIOM-SSB-relative	Unknown	Unknown	BIOM-SSB	Unknown	Mortality rate / Mortality rate from fishing (F)	BIOM-SSB	R	Ratio SSB/R	Mortality rate / Mortality rate from fishing (F)	BIOM-SSB	R	Ratio SSB/R
Threshold value upper													0.31	150000.0	3776242.0	0.039				0.26	23492.0	79211.0	0.543		120637.0	2500530.0	0.035							1.0									1.0						0.31	4730.0	36603.0	0.166	1.0	0.5																				0.26	2600.0	3691.0	0.364	0.31	570000.0	50530055.0	0.016
Threshold value lower
Threshold value operator													<=	>=	>=	>=				<=	>=	>=	>=		>=	>=	>=							>=									>=						<=	>=	>=	>=	<=	>=																				<=	>=	>=	>=	<=	>=	>=	>=
Threshold qualitative
Threshold value source													ICES	ICES	National	National				ICES	ICES	National	National		ICES	National	National																ICES						ICES	ICES	National	National	ICES	ICES																				ICES	ICES	National	National		ICES	National	National
Value achieved upper													0.356	64048.0	761782.0	0.086				0.92	9956.0	15093.0	2.317		81038.0	1862287.0	0.049							1.4									1.4	65.79			149.0		0.42	9835.0	80163.0	0.178	0.266	1.744																				0.211	2513.0	2214.0	1.317	0.381	976167.0	76717333.0	0.013
Value achieved lower
Value unit													Rate/y	tonne	individuals	Proportion				Rate/y	tonne	individuals	Proportion	Rate/y	tonne	individuals	Proportion																	Catch-Per-Unit-Effort			Catch-Per-Unit-Effort		Rate/y	tonne	individuals	Proportion	Proportion	Proportion																				Rate/y	tonne	individuals	Proportion	Rate/y	tonne	individuals	Proportion
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend parameter	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Stable	Stable	Stable	Stable	Unknown	Unknown	Unknown	Stable	Stable	Stable	Stable	Improving	Deteriorating	Deteriorating	Stable	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Stable	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Stable	Not relevant	Unknown		Not relevant	Unknown	Stable	Stable	Improving	Stable	Stable	Stable	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Not relevant	Unknown	Unknown	Not relevant	Unknown	Stable	Stable	Stable	Stable	Stable	Stable	Stable	Stable
Parameter achieved	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	No	No	No	Yes	Unknown	Unknown	Unknown	No	No	No	Yes	Unknown	No	No	Yes	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Yes	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Yes	Not assessed	Unknown		Not assessed	Unknown	No	Yes	Yes	Yes	Yes	Yes	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Not assessed	Unknown	Unknown	Not assessed	Unknown	Yes	No	No	Yes	No	Yes	Yes	No
Description parameter																												The trend has not been assessed.
Related indicator													Herring (Clupea harengus) in Subdivisions 20-24, spring spawners (Skagerrak, Kattegat, and western Baltic)	Herring (Clupea harengus) in Subdivisions 20-24, spring spawners (Skagerrak, Kattegat, and western Baltic)	NAT-BALDE-R-SSB/R	NAT-BALDE-R-SSB/R				Cod (Gadus morhua) in Subdivisions 22-24, western Baltic stock (western Baltic Sea)	Cod (Gadus morhua) in Subdivisions 22-24, western Baltic stock (western Baltic Sea)	NAT-BALDE-R-SSB/R	NAT-BALDE-R-SSB/R	Cod (Gadus morhua) in Subdivisions 24-32, eastern Baltic stock (eastern Baltic Sea)	Cod (Gadus morhua) in Subdivisions 24-32, eastern Baltic stock (eastern Baltic Sea)	NAT-BALDE-R-SSB/R	NAT-BALDE-R-SSB/R																	Flounder (Platichthys flesus) in Subdivisions 22 and 23 (Belt Seas and the Sound)					Plaice (Pleuronectes platessa) in Subdivisions 21-23 (Kattegat, Belt Seas, and the Sound)	Plaice (Pleuronectes platessa) in Subdivisions 21-23 (Kattegat, Belt Seas, and the Sound)	NAT-BALDE-R-SSB/R	NAT-BALDE-R-SSB/R	Plaice (Pleuronectes platessa) in Subdivisions 24-32 (Baltic Sea, excluding the Sound and Belt Seas)	Plaice (Pleuronectes platessa) in Subdivisions 24-32 (Baltic Sea, excluding the Sound and Belt Seas)															Turbot (Scophthalmus maximus) in Subdivisions 22-32 (Baltic Sea)							NAT-BALDE-R-SSB/R	NAT-BALDE-R-SSB/R	Sprat (Sprattus sprattus) in Subdivisions 22-32 (Baltic Sea)	Sprat (Sprattus sprattus) in Subdivisions 22-32 (Baltic Sea)	NAT-BALDE-R-SSB/R	NAT-BALDE-R-SSB/R
Criteria status	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Not good	Not good	Not good	Not good	Unknown	Unknown	Unknown	Not good	Not good	Not good	Not good	Unknown	Not good	Not good	Not good	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Good	Not assessed	Unknown	Good	Unknown	Unknown	Not good	Good	Good	Good	Good	Good	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Good	Not good	Not good	Not good	Not good	Good	Not good	Not good
Description criteria															Neue Bewertung anhand Rekrutierung (R) und SSB/R, siehe Probst, W. N. 2023. An approach to assess exploited fish stocks compliant to the requirements of the Marine Strategy Framework Directive (MSFD) including criterion D3C3. Ecological Indicators, 146.	Neue Bewertung anhand Rekrutierung (R) und SSB/R, siehe Probst, W. N. 2023. An approach to assess exploited fish stocks compliant to the requirements of the Marine Strategy Framework Directive (MSFD) including criterion D3C3. Ecological Indicators, 146.						Neue Bewertung anhand Rekrutierung (R) und SSB/R, siehe Probst, W. N. 2023. An approach to assess exploited fish stocks compliant to the requirements of the Marine Strategy Framework Directive (MSFD) including criterion D3C3. Ecological Indicators, 146.	Neue Bewertung anhand Rekrutierung (R) und SSB/R, siehe Probst, W. N. 2023. An approach to assess exploited fish stocks compliant to the requirements of the Marine Strategy Framework Directive (MSFD) including criterion D3C3. Ecological Indicators, 146.			Neue Bewertung anhand Rekrutierung (R) und SSB/R, siehe Probst, W. N. 2023. An approach to assess exploited fish stocks compliant to the requirements of the Marine Strategy Framework Directive (MSFD) including criterion D3C3. Ecological Indicators, 146.	Neue Bewertung anhand Rekrutierung (R) und SSB/R, siehe Probst, W. N. 2023. An approach to assess exploited fish stocks compliant to the requirements of the Marine Strategy Framework Directive (MSFD) including criterion D3C3. Ecological Indicators, 146.																								Neue Bewertung anhand Rekrutierung (R) und SSB/R, siehe Probst, W. N. 2023. An approach to assess exploited fish stocks compliant to the requirements of the Marine Strategy Framework Directive (MSFD) including criterion D3C3. Ecological Indicators, 146.	Neue Bewertung anhand Rekrutierung (R) und SSB/R, siehe Probst, W. N. 2023. An approach to assess exploited fish stocks compliant to the requirements of the Marine Strategy Framework Directive (MSFD) including criterion D3C3. Ecological Indicators, 146.																												Neue Bewertung anhand Rekrutierung (R) und SSB/R, siehe Probst, W. N. 2023. An approach to assess exploited fish stocks compliant to the requirements of the Marine Strategy Framework Directive (MSFD) including criterion D3C3. Ecological Indicators, 146.	Neue Bewertung anhand Rekrutierung (R) und SSB/R, siehe Probst, W. N. 2023. An approach to assess exploited fish stocks compliant to the requirements of the Marine Strategy Framework Directive (MSFD) including criterion D3C3. Ecological Indicators, 146.
Element status	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Not good	Not good	Not good	Unknown	Unknown	Unknown	Not good	Not good	Not good	Not good	Unknown	Unknown	Unknown	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Not good	Not good	Not good	Not good	Good	Good	Good	Unknown	Unknown	Unknown	Not good	Not good	Not good	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good
Description element	No evaluation results are available for this element.	No evaluation results are available for this element.	No evaluation results are available for this element.	No evaluation results are available for this element.	No evaluation results are available for this element.	No evaluation results are available for this element.	Expert assessment based on ICES Advice 2022	Expert assessment based on ICES Advice 2022	Expert assessment based on ICES Advice 2022	No valuations are available for this element.	No valuations are available for this element.	No valuations are available for this element.					No evaluation results are available for this element.	No evaluation results are available for this element.	No evaluation results are available for this element.									No valuations are available for this element.	No valuations are available for this element.	No valuations are available for this element.	No evaluation results are available for this element.	No evaluation results are available for this element.	No evaluation results are available for this element.	No evaluation results are available for this element.	No evaluation results are available for this element.	No evaluation results are available for this element.	No evaluation results are available for this element.	No evaluation results are available for this element.	No evaluation results are available for this element.	No evaluation results are available for this element.	No evaluation results are available for this element.	No evaluation results are available for this element.				This refers to Baltic flounder Platichthys solemdali.	This refers to Baltic flounder Platichthys solemdali.	This refers to Baltic flounder Platichthys solemdali.								No evaluation results are available for this element.	No evaluation results are available for this element.	No evaluation results are available for this element.	Expert assessment based on ICES Advice 2022	Expert assessment based on ICES Advice 2022	Expert assessment based on ICES Advice 2022	No evaluation results are available for this element.	No evaluation results are available for this element.	No evaluation results are available for this element.	No evaluation results are available for this element.	No evaluation results are available for this element.	No evaluation results are available for this element.	No valuations are available for this element.	No valuations are available for this element.	No valuations are available for this element.
Source assessment feature	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES	ICES
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	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	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	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	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	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating	Deteriorating
Integration rule type parameter	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	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 parameter
Integration rule type criteria	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other
Integration rule description criteria	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.	For the MSFD status assessment, the indicator values of fishing mortality (criterion D3C1), spawning stock biomass (criterion D3C2) and age structure (criterion D3C3) are averaged over the period 2016-2021 and compared against the reference values. The individual assessments of the three criteria will be integrated in a two-step process. Criteria D3C1 and D3C2 are first integrated according to the ‘one out – all out’ principle. Criterion D3C3 cannot improve the integrated assessment of D3C1 and D3C2, but only confirm or downgrade.
GES extent threshold
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	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	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	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	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	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	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	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	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	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	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.	One stock has good environmental status, eight stocks do not have good environmental status and 16 stocks could not be assessed due to a lack of indicators or assessment limits.
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	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	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)	Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
Related targets	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4	UZO4.1 UZO4.2 UZO4.4
Test TV	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	No	No	No	Yes	NA	NA	NA	No	No	No	Yes	NA	No	No	Yes	NA	NA	NA	NA	NA	NA	Yes	NA	NA	NA	NA	NA	NA	NA	NA	Yes	NA	NA	NA	NA	NA	No	Yes	Yes	Yes	Yes	Yes	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	Yes	No	No	Yes	No	Yes	Yes	No
Test results	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	False	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct