MS/Art8-2024/2024/D3/Italy/Mediterranean: Ionian Sea & Central Mediterranean Sea

Member State report / Art8-2024 / 2024 / D3 / Italy / Mediterranean: Ionian Sea & Central Mediterranean 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	Italy
Region/subregion	Mediterranean: Ionian Sea & Central Mediterranean Sea
Report date	2025-09-11 10:38:38

MIC-IT-MS-ISCMS

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	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	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish
Element	Aristaeomorpha foliacea	Aristaeomorpha foliacea	Aristeus antennatus	Aristeus antennatus	Aristeus antennatus	Boops boops	Boops boops	Boops boops	Chelidonichthys lucerna	Chelidonichthys lucerna	Chelidonichthys lucerna	Diplodus annularis	Diplodus annularis	Diplodus annularis	Diplodus vulgaris	Diplodus vulgaris	Diplodus vulgaris	Eledone cirrhosa	Eledone cirrhosa	Eledone cirrhosa	Eledone moschata	Eledone moschata	Eledone moschata	Engraulis encrasicolus	Engraulis encrasicolus	Engraulis encrasicolus	Helicolenus dactylopterus	Helicolenus dactylopterus	Helicolenus dactylopterus	Illex coindetii	Illex coindetii	Illex coindetii	Lepidopus caudatus	Lepidopus caudatus	Lepidopus caudatus	Loligo vulgaris	Loligo vulgaris	Loligo vulgaris	Lophius budegassa	Lophius budegassa	Lophius budegassa	Merluccius merluccius	Merluccius merluccius	Mullus barbatus	Mullus barbatus	Mullus barbatus	Mullus surmuletus	Mullus surmuletus	Mullus surmuletus	Nephrops norvegicus	Nephrops norvegicus	Nephrops norvegicus	Octopus vulgaris	Octopus vulgaris	Octopus vulgaris	Pagellus acarne	Pagellus acarne	Pagellus acarne	Pagellus erythrinus	Pagellus erythrinus	Pagellus erythrinus	Parapenaeus longirostris	Parapenaeus longirostris	Raja clavata	Raja clavata	Raja clavata	Sardina pilchardus	Sardina pilchardus	Sardina pilchardus	Scorpaena scrofa	Scorpaena scrofa	Scorpaena scrofa	Sepia officinalis	Sepia officinalis	Sepia officinalis	Squilla mantis	Squilla mantis	Squilla mantis	Trachurus mediterraneus	Trachurus mediterraneus	Trachurus mediterraneus	Trachurus trachurus	Trachurus trachurus	Trachurus trachurus
Element extent
Trend element	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown
Element 2	Giant red shrimp (Aristaemorpha foliacea) in GSAs 12-13-14-15-16-21w	Giant red shrimp (Aristaemorpha foliacea) in GSAs 12-13-14-15-16-21w	Blue and red shrimp (Aristeus antennatus) in GSA 16 (Southern Sicily)	Blue and red shrimp (Aristeus antennatus) in GSA 16 (Southern Sicily)	Blue and red shrimp (Aristeus antennatus) in GSA 16 (Southern Sicily)	Bogue (Boops boops) in GSA 16 (Southern Sicily)	Bogue (Boops boops) in GSA 16 (Southern Sicily)	Bogue (Boops boops) in GSA 16 (Southern Sicily)	Tub gurnard (Chelidonichthys lucerna) in GSA 16 (Southern Sicily)	Tub gurnard (Chelidonichthys lucerna) in GSA 16 (Southern Sicily)	Tub gurnard (Chelidonichthys lucerna) in GSA 16 (Southern Sicily)	Annular seabream (Diplodus annularis) in GSA 16 (Southern Sicily)	Annular seabream (Diplodus annularis) in GSA 16 (Southern Sicily)	Annular seabream (Diplodus annularis) in GSA 16 (Southern Sicily)	Common two-banded seabream (Diplodus vulgaris) in GSA 16 (Southern Sicily)	Common two-banded seabream (Diplodus vulgaris) in GSA 16 (Southern Sicily)	Common two-banded seabream (Diplodus vulgaris) in GSA 16 (Southern Sicily)	Horned octopus (Eledone cirrhosa) in GSA 16 (Southern Sicily)	Horned octopus (Eledone cirrhosa) in GSA 16 (Southern Sicily)	Horned octopus (Eledone cirrhosa) in GSA 16 (Southern Sicily)	Musky octopus (Eledone moschata) in GSA 16 (Southern Sicily)	Musky octopus (Eledone moschata) in GSA 16 (Southern Sicily)	Musky octopus (Eledone moschata) in GSA 16 (Southern Sicily)	Anchovy (Engraulis encrasicolus) in GSA 16 (Southern Sicily)	Anchovy (Engraulis encrasicolus) in GSA 16 (Southern Sicily)	Anchovy (Engraulis encrasicolus) in GSA 16 (Southern Sicily)	Blackbelly rosefish (Helicolenus dactylopterus) in GSA 16 (Southern Sicily)	Blackbelly rosefish (Helicolenus dactylopterus) in GSA 16 (Southern Sicily)	Blackbelly rosefish (Helicolenus dactylopterus) in GSA 16 (Southern Sicily)	Broadtail shortfin squid (Illex coindetii) in GSA 16 (Southern Sicily)	Broadtail shortfin squid (Illex coindetii) in GSA 16 (Southern Sicily)	Broadtail shortfin squid (Illex coindetii) in GSA 16 (Southern Sicily)	Silver scabbardfish (Lepidopus caudatus) in GSA 16 (Southern Sicily)	Silver scabbardfish (Lepidopus caudatus) in GSA 16 (Southern Sicily)	Silver scabbardfish (Lepidopus caudatus) in GSA 16 (Southern Sicily)	European squid (Loligo vulgaris) in GSA 16 (Southern Sicily)	European squid (Loligo vulgaris) in GSA 16 (Southern Sicily)	European squid (Loligo vulgaris) in GSA 16 (Southern Sicily)	Black-bellied anglerfish (Lophius budegassa) in GSA 16 (Southern Sicily)	Black-bellied anglerfish (Lophius budegassa) in GSA 16 (Southern Sicily)	Black-bellied anglerfish (Lophius budegassa) in GSA 16 (Southern Sicily)	European hake (Merluccius merluccius) in GSAs 12-13-14-15-16	European hake (Merluccius merluccius) in GSAs 12-13-14-15-16	Red mullet (Mullus barbatus) in GSA 16 (Southern Sicily)	Red mullet (Mullus barbatus) in GSA 16 (Southern Sicily)	Red mullet (Mullus barbatus) in GSA 16 (Southern Sicily)	Striped red mullet (Mullus surmuletus) in GSA 16 (Southern Sicily)	Striped red mullet (Mullus surmuletus) in GSA 16 (Southern Sicily)	Striped red mullet (Mullus surmuletus) in GSA 16 (Southern Sicily)	Norway lobster (Nephrops norvegicus) in GSA 16 (Southern Sicily)	Norway lobster (Nephrops norvegicus) in GSA 16 (Southern Sicily)	Norway lobster (Nephrops norvegicus) in GSA 16 (Southern Sicily)	Common octopus (Octopus vulgaris) in GSA 16 (Southern Sicily)	Common octopus (Octopus vulgaris) in GSA 16 (Southern Sicily)	Common octopus (Octopus vulgaris) in GSA 16 (Southern Sicily)	Axillary seabream (Pagellus acarne) in GSA 16 (Southern Sicily)	Axillary seabream (Pagellus acarne) in GSA 16 (Southern Sicily)	Axillary seabream (Pagellus acarne) in GSA 16 (Southern Sicily)	Common pandora (Pagellus erythrinus) in GSA 16 (Southern Sicily)	Common pandora (Pagellus erythrinus) in GSA 16 (Southern Sicily)	Common pandora (Pagellus erythrinus) in GSA 16 (Southern Sicily)	Deep-water rose shrimp (Parapenaeus longirostris) in GSAs 12-13-14-15-16	Deep-water rose shrimp (Parapenaeus longirostris) in GSAs 12-13-14-15-16	Thornback ray (Raja clavata) in GSA 16 (Southern Sicily)	Thornback ray (Raja clavata) in GSA 16 (Southern Sicily)	Thornback ray (Raja clavata) in GSA 16 (Southern Sicily)	Sardine (Sardina Pilchardus) in GSA 16 (Southern Sicily)	Sardine (Sardina Pilchardus) in GSA 16 (Southern Sicily)	Sardine (Sardina Pilchardus) in GSA 16 (Southern Sicily)	Red scorpionfish (Scorpaena scrofa) in GSA 16 (Southern Sicily)	Red scorpionfish (Scorpaena scrofa) in GSA 16 (Southern Sicily)	Red scorpionfish (Scorpaena scrofa) in GSA 16 (Southern Sicily)	Common cuttlefish (Sepia officinalis) in GSA 16 (Southern Sicily)	Common cuttlefish (Sepia officinalis) in GSA 16 (Southern Sicily)	Common cuttlefish (Sepia officinalis) in GSA 16 (Southern Sicily)	Spottail mantis squillid (Squilla mantis) in GSA 16 (Southern Sicily)	Spottail mantis squillid (Squilla mantis) in GSA 16 (Southern Sicily)	Spottail mantis squillid (Squilla mantis) in GSA 16 (Southern Sicily)	Mediterranean horse mackerel (Trachurus mediterraneus) in GSA 16 (Southern Sicily)	Mediterranean horse mackerel (Trachurus mediterraneus) in GSA 16 (Southern Sicily)	Mediterranean horse mackerel (Trachurus mediterraneus) in GSA 16 (Southern Sicily)	Atlantic horse mackerel (Trachurus trachurus) in GSA 16 (Southern Sicily)	Atlantic horse mackerel (Trachurus trachurus) in GSA 16 (Southern Sicily)	Atlantic horse mackerel (Trachurus trachurus) in GSA 16 (Southern Sicily)
Element source	GFCM	GFCM	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	GFCM	GFCM	GFCM	GFCM	GFCM	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	GFCM	GFCM	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National
Criterion	D3C1	D3C2	D3C1	D3C2	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	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3
Parameter	Fcurr/Fref	SSBcurr/SSBref	Fcurr/Fref	SSBcurr/SSBref	L90%/L90inf	Fcurr/Fref	SSBcurr/SSBref	L90%/L90inf	Fcurr/Fref	SSBcurr/SSBref	L90%/L90inf	Fcurr/Fref	SSBcurr/SSBref	L90%/L90inf	Fcurr/Fref	SSBcurr/SSBref	L90%/L90inf	Fcurr/Fref	SSBcurr/SSBref	L90%/L90inf	Fcurr/Fref	SSBcurr/SSBref	L90%/L90inf	Fcurr/Fref	SSBcurr/SSBref	L90%/L90inf	Fcurr/Fref	SSBcurr/SSBref	L90%/L90inf	Fcurr/Fref	SSBcurr/SSBref	L90%/L90inf	Fcurr/Fref	SSBcurr/SSBref	L90%/L90inf	Fcurr/Fref	SSBcurr/SSBref	L90%/L90inf	Fcurr/Fref	SSBcurr/SSBref	L90%/L90inf	Fcurr/Fref	SSBcurr/SSBref	Fcurr/Fref	SSBcurr/SSBref	L90%/L90inf	Fcurr/Fref	SSBcurr/SSBref	L90%/L90inf	Fcurr/Fref	SSBcurr/SSBref	L90%/L90inf	Fcurr/Fref	SSBcurr/SSBref	L90%/L90inf	Fcurr/Fref	SSBcurr/SSBref	L90%/L90inf	Fcurr/Fref	SSBcurr/SSBref	L90%/L90inf	Fcurr/Fref	SSBcurr/SSBref	Fcurr/Fref	SSBcurr/SSBref	L90%/L90inf	Fcurr/Fref	SSBcurr/SSBref	L90%/L90inf	Fcurr/Fref	SSBcurr/SSBref	L90%/L90inf	Fcurr/Fref	SSBcurr/SSBref	L90%/L90inf	Fcurr/Fref	SSBcurr/SSBref	L90%/L90inf	Fcurr/Fref	SSBcurr/SSBref	L90%/L90inf	Fcurr/Fref	SSBcurr/SSBref	L90%/L90inf
Threshold value upper	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0	1.0
Threshold value lower
Threshold value operator	<=	>	<=	>	>	<=	>	>	<=	>	>	<=	>	>	<=	>	>	<=	>	>	<=	>	>	<=	>	>	<=	>	>	<=	>	>	<=	>	>	<=	>	>	<=	>	>	<=	>	<=	>	>	<=	>	>	<=	>	>	<=	>	>	<=	>	>	<=	>	>	<=	>	<=	>	>	<=	>	>	<=	>	>	<=	>	>	<=	>	>	<=	>	>	<=	>	>
Threshold qualitative
Threshold value source	Common Fisheries Policy	Common Fisheries Policy	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	Common Fisheries Policy	Common Fisheries Policy	Common Fisheries Policy	Common Fisheries Policy	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	Common Fisheries Policy	Common Fisheries Policy	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National	National
Value achieved upper	1.29	0.68	2.01	0.43	0.84	1.13	0.22	0.62	1.25	0.79	0.58	1.3	0.48		0.25	1.52		2.06	0.1	0.86	2.17	0.25	0.82	0.85	0.88	1.0	1.86	0.66		0.82	1.08	0.8	1.47	0.19		1.41	0.84	0.45	1.39	0.85	0.83	1.06	0.93	0.8		0.99	1.8	0.28	0.97	2.62	1.37	0.79	1.81	0.39	0.59	0.59	1.36		0.86	0.63	0.59	1.12	0.79	0.88	1.05	0.7	0.83	0.16	0.85	0.35	1.67		1.05	0.94	0.61	1.12	1.21		1.77	0.51		0.48	0.76	0.65
Value achieved lower
Value unit	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional		Adimensional	Adimensional		Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional		Adimensional	Adimensional	Adimensional	Adimensional	Adimensional		Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional		Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional		Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional	Adimensional		Adimensional	Adimensional	Adimensional	Adimensional	Adimensional		Adimensional	Adimensional		Adimensional	Adimensional	Adimensional
Proportion threshold value	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0	100.0
Proportion value achieved
Proportion threshold value unit	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value	% of population achieving threshold value
Trend parameter	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Improving	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown	Unknown
Parameter achieved	No	No	No	No	Unknown	No	No	Unknown	No	No	Unknown	No	No	Unknown	Yes	Yes	Unknown	No	No	Unknown	No	No	Unknown	Yes	No	Unknown	No	No	Unknown	Yes	Yes	Unknown	No	No	Unknown	No	No	Unknown	No	No	Unknown	No	No	Yes	Unknown	Unknown	No	No	Unknown	No	Yes	Unknown	No	No	Unknown	Yes	Yes	Unknown	Yes	No	Unknown	No	No	Yes	Yes	Unknown	Yes	No	Unknown	Yes	Yes	Unknown	No	No	Unknown	No	Yes	Unknown	No	No	Unknown	Yes	No	Unknown
Description parameter	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	For the subregions MWE and MIC the parameter used to assess the status of individual stocks according to criterion D3C3 was calculated as follows: the average ratio of L90 (the length at the 90th percentile of the size structure) to Linf (the length that fish in a population would reach if they grew indefinitely) over the years 2016-2021, compared to the expected value of 0.8. This parameter is denoted as L90%/Linf	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	For the subregions MWE and MIC the parameter used to assess the status of individual stocks according to criterion D3C3 was calculated as follows: the average ratio of L90 (the length at the 90th percentile of the size structure) to Linf (the length that fish in a population would reach if they grew indefinitely) over the years 2016-2021, compared to the expected value of 0.8. This parameter is denoted as L90%/Linf	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	For the subregions MWE and MIC the parameter used to assess the status of individual stocks according to criterion D3C3 was calculated as follows: the average ratio of L90 (the length at the 90th percentile of the size structure) to Linf (the length that fish in a population would reach if they grew indefinitely) over the years 2016-2021, compared to the expected value of 0.8. This parameter is denoted as L90%/Linf	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	For the subregions MWE and MIC the parameter used to assess the status of individual stocks according to criterion D3C3 was calculated as follows: the average ratio of L90 (the length at the 90th percentile of the size structure) to Linf (the length that fish in a population would reach if they grew indefinitely) over the years 2016-2021, compared to the expected value of 0.8. This parameter is denoted as L90%/Linf	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	For the subregions MWE and MIC the parameter used to assess the status of individual stocks according to criterion D3C3 was calculated as follows: the average ratio of L90 (the length at the 90th percentile of the size structure) to Linf (the length that fish in a population would reach if they grew indefinitely) over the years 2016-2021, compared to the expected value of 0.8. This parameter is denoted as L90%/Linf	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	For the subregions MWE and MIC the parameter used to assess the status of individual stocks according to criterion D3C3 was calculated as follows: the average ratio of L90 (the length at the 90th percentile of the size structure) to Linf (the length that fish in a population would reach if they grew indefinitely) over the years 2016-2021, compared to the expected value of 0.8. This parameter is denoted as L90%/Linf	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	For the subregions MWE and MIC the parameter used to assess the status of individual stocks according to criterion D3C3 was calculated as follows: the average ratio of L90 (the length at the 90th percentile of the size structure) to Linf (the length that fish in a population would reach if they grew indefinitely) over the years 2016-2021, compared to the expected value of 0.8. This parameter is denoted as L90%/Linf	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	For the subregions MWE and MIC the parameter used to assess the status of individual stocks according to criterion D3C3 was calculated as follows: the average ratio of L90 (the length at the 90th percentile of the size structure) to Linf (the length that fish in a population would reach if they grew indefinitely) over the years 2016-2021, compared to the expected value of 0.8. This parameter is denoted as L90%/Linf	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	For the subregions MWE and MIC the parameter used to assess the status of individual stocks according to criterion D3C3 was calculated as follows: the average ratio of L90 (the length at the 90th percentile of the size structure) to Linf (the length that fish in a population would reach if they grew indefinitely) over the years 2016-2021, compared to the expected value of 0.8. This parameter is denoted as L90%/Linf	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	For the subregions MWE and MIC the parameter used to assess the status of individual stocks according to criterion D3C3 was calculated as follows: the average ratio of L90 (the length at the 90th percentile of the size structure) to Linf (the length that fish in a population would reach if they grew indefinitely) over the years 2016-2021, compared to the expected value of 0.8. This parameter is denoted as L90%/Linf	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	For the subregions MWE and MIC the parameter used to assess the status of individual stocks according to criterion D3C3 was calculated as follows: the average ratio of L90 (the length at the 90th percentile of the size structure) to Linf (the length that fish in a population would reach if they grew indefinitely) over the years 2016-2021, compared to the expected value of 0.8. This parameter is denoted as L90%/Linf	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	For the subregions MWE and MIC the parameter used to assess the status of individual stocks according to criterion D3C3 was calculated as follows: the average ratio of L90 (the length at the 90th percentile of the size structure) to Linf (the length that fish in a population would reach if they grew indefinitely) over the years 2016-2021, compared to the expected value of 0.8. This parameter is denoted as L90%/Linf	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	For the subregions MWE and MIC the parameter used to assess the status of individual stocks according to criterion D3C3 was calculated as follows: the average ratio of L90 (the length at the 90th percentile of the size structure) to Linf (the length that fish in a population would reach if they grew indefinitely) over the years 2016-2021, compared to the expected value of 0.8. This parameter is denoted as L90%/Linf	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	For the subregions MWE and MIC the parameter used to assess the status of individual stocks according to criterion D3C3 was calculated as follows: the average ratio of L90 (the length at the 90th percentile of the size structure) to Linf (the length that fish in a population would reach if they grew indefinitely) over the years 2016-2021, compared to the expected value of 0.8. This parameter is denoted as L90%/Linf	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	For the subregions MWE and MIC the parameter used to assess the status of individual stocks according to criterion D3C3 was calculated as follows: the average ratio of L90 (the length at the 90th percentile of the size structure) to Linf (the length that fish in a population would reach if they grew indefinitely) over the years 2016-2021, compared to the expected value of 0.8. This parameter is denoted as L90%/Linf	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	For the subregions MWE and MIC the parameter used to assess the status of individual stocks according to criterion D3C3 was calculated as follows: the average ratio of L90 (the length at the 90th percentile of the size structure) to Linf (the length that fish in a population would reach if they grew indefinitely) over the years 2016-2021, compared to the expected value of 0.8. This parameter is denoted as L90%/Linf	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	For the subregions MWE and MIC the parameter used to assess the status of individual stocks according to criterion D3C3 was calculated as follows: the average ratio of L90 (the length at the 90th percentile of the size structure) to Linf (the length that fish in a population would reach if they grew indefinitely) over the years 2016-2021, compared to the expected value of 0.8. This parameter is denoted as L90%/Linf	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	For the subregions MWE and MIC the parameter used to assess the status of individual stocks according to criterion D3C3 was calculated as follows: the average ratio of L90 (the length at the 90th percentile of the size structure) to Linf (the length that fish in a population would reach if they grew indefinitely) over the years 2016-2021, compared to the expected value of 0.8. This parameter is denoted as L90%/Linf	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	For the subregions MWE and MIC the parameter used to assess the status of individual stocks according to criterion D3C3 was calculated as follows: the average ratio of L90 (the length at the 90th percentile of the size structure) to Linf (the length that fish in a population would reach if they grew indefinitely) over the years 2016-2021, compared to the expected value of 0.8. This parameter is denoted as L90%/Linf	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	For the subregions MWE and MIC the parameter used to assess the status of individual stocks according to criterion D3C3 was calculated as follows: the average ratio of L90 (the length at the 90th percentile of the size structure) to Linf (the length that fish in a population would reach if they grew indefinitely) over the years 2016-2021, compared to the expected value of 0.8. This parameter is denoted as L90%/Linf	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	For the subregions MWE and MIC the parameter used to assess the status of individual stocks according to criterion D3C3 was calculated as follows: the average ratio of L90 (the length at the 90th percentile of the size structure) to Linf (the length that fish in a population would reach if they grew indefinitely) over the years 2016-2021, compared to the expected value of 0.8. This parameter is denoted as L90%/Linf	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	For the subregions MWE and MIC the parameter used to assess the status of individual stocks according to criterion D3C3 was calculated as follows: the average ratio of L90 (the length at the 90th percentile of the size structure) to Linf (the length that fish in a population would reach if they grew indefinitely) over the years 2016-2021, compared to the expected value of 0.8. This parameter is denoted as L90%/Linf	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	For the subregions MWE and MIC the parameter used to assess the status of individual stocks according to criterion D3C3 was calculated as follows: the average ratio of L90 (the length at the 90th percentile of the size structure) to Linf (the length that fish in a population would reach if they grew indefinitely) over the years 2016-2021, compared to the expected value of 0.8. This parameter is denoted as L90%/Linf	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	For the subregions MWE and MIC the parameter used to assess the status of individual stocks according to criterion D3C3 was calculated as follows: the average ratio of L90 (the length at the 90th percentile of the size structure) to Linf (the length that fish in a population would reach if they grew indefinitely) over the years 2016-2021, compared to the expected value of 0.8. This parameter is denoted as L90%/Linf	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	For the subregions MWE and MIC the parameter used to assess the status of individual stocks according to criterion D3C3 was calculated as follows: the average ratio of L90 (the length at the 90th percentile of the size structure) to Linf (the length that fish in a population would reach if they grew indefinitely) over the years 2016-2021, compared to the expected value of 0.8. This parameter is denoted as L90%/Linf	The parameter used to assess the status of individual stocks according to criterion D3C1 was calculated as the average of the ratio of Fcurr (current fishing mortality) to Fref (fishing mortality at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as Fcurr/Fref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	The parameter used to assess the status of individual stocks according to criterion D3C2 was calculated as the average of the ratio of SSB (Spawning stock biomass or Biomass of the stock) to SSBref (Spawning stock biomass or Biomass of the stock at maximum sustainable yield, MSY, or its proxy) over the years 2016-2021. This parameter is denoted as SSBcurr/SSBref (avg 6 yrs, '16-'21). The parameter was estimated when at least 4 out of 6 years data were available.	For the subregions MWE and MIC the parameter used to assess the status of individual stocks according to criterion D3C3 was calculated as follows: the average ratio of L90 (the length at the 90th percentile of the size structure) to Linf (the length that fish in a population would reach if they grew indefinitely) over the years 2016-2021, compared to the expected value of 0.8. This parameter is denoted as L90%/Linf
Related indicator	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3	MIC-IT-MS-ISCMS-D3
Criteria status	Not good	Not good	Not good	Not good	Unknown	Not good	Not good	Unknown	Not good	Not good	Unknown	Not good	Not good	Unknown	Good	Good	Unknown	Not good	Not good	Unknown	Not good	Not good	Unknown	Good	Not good	Unknown	Not good	Not good	Unknown	Good	Good	Unknown	Not good	Not good	Unknown	Not good	Not good	Unknown	Not good	Not good	Unknown	Not good	Not good	Good	Unknown	Unknown	Not good	Not good	Unknown	Not good	Good	Unknown	Not good	Not good	Unknown	Good	Good	Unknown	Good	Not good	Unknown	Not good	Not good	Good	Good	Unknown	Good	Not good	Unknown	Good	Good	Unknown	Not good	Not good	Unknown	Not good	Good	Unknown	Not good	Not good	Unknown	Good	Not good	Unknown
Description criteria	High confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments validated at the international level (STECF or GFCM).	High confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments validated at the international level (STECF or GFCM).	Low confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods relying only on fisheries-independent data (AMSY).	Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).		Low confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods relying only on fisheries-independent data (AMSY).	Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).		Low confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods relying only on fisheries-independent data (AMSY).	Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).		Low confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods relying only on fisheries-independent data (AMSY).	Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).		Low confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods relying only on fisheries-independent data (AMSY).	Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).		Low confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods relying only on fisheries-independent data (AMSY).	Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).		Low confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods relying only on fisheries-independent data (AMSY).	Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).		Medium confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).	Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).		Low confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods relying only on fisheries-independent data (AMSY).	Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).		Medium confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).	Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).		Low confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods relying only on fisheries-independent data (AMSY).	Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).		Low confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods relying only on fisheries-independent data (AMSY).	Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).		Low confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods relying only on fisheries-independent data (AMSY).	Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).		High confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments validated at the international level (STECF or GFCM).	High confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments validated at the international level (STECF or GFCM).	High confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments validated at the international level (STECF or GFCM).			Low confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods relying only on fisheries-independent data (AMSY).	Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).		Medium confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).	Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).		Low confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods relying only on fisheries-independent data (AMSY).	Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).		Low confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods relying only on fisheries-independent data (AMSY).	Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).		Medium confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).	Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).		High confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments validated at the international level (STECF or GFCM).	High confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments validated at the international level (STECF or GFCM).	Medium confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).	Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).		Low confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods relying only on fisheries-independent data (AMSY).	Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).		Low confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods relying only on fisheries-independent data (AMSY).	Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).		Medium confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).	Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).		Medium confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).	Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).		Low confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods relying only on fisheries-independent data (AMSY).	Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).		Medium confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).	Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).
Element status	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Good	Good	Good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Good	Good	Good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	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	Not good	Good	Good	Good	Not good	Not good	Not good	Not good	Not good	Good	Good	Good	Not good	Not good	Not good	Good	Good	Good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good	Not good
Description element
Source assessment feature	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	National	National	National
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	Type C	Type C	Type C
Trend feature	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving	Improving
Integration rule type parameter	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant
Integration rule description parameter	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant	Not relevant
Integration rule type criteria	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE	TREE
Integration rule description criteria	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)	EU (MSFD CIS D3)
GES extent threshold	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00	1.00
GES extent achieved
GES extent unit	Proportion of populations in good status	Proportion of populations in good status	Proportion of populations in good status	Proportion of populations in good status	Proportion of populations in good status	Proportion of populations in good status	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	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported	GES later than 2024, Art14ExceptionNotReported
Description overall status
Assessments period	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	2016-2021	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)	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	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 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MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005	MIC-IT-D03-T001 MIC-IT-D03-T002 MIC-IT-D03-T003 MIC-IT-D03-T004 MIC-IT-D03-T005
Test TV	No	No	No	No	No	No	No	No	No	No	No	No	No	NA	Yes	Yes	NA	No	No	No	No	No	No	Yes	No	No	No	No	NA	Yes	Yes	No	No	No	NA	No	No	No	No	No	No	No	No	Yes	NA	No	No	No	No	No	Yes	No	No	No	No	Yes	Yes	NA	Yes	No	No	No	No	Yes	Yes	No	Yes	No	No	Yes	Yes	NA	No	No	No	No	Yes	NA	No	No	NA	Yes	No	No
Test results	Correct	Correct	Correct	Correct	False	Correct	Correct	False	Correct	Correct	False	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	False	Correct	Correct	False	Correct	Correct	False	Correct	Correct	Correct	Correct	Correct	False	Correct	Correct	Correct	Correct	Correct	False	Correct	Correct	False	Correct	Correct	Correct	Correct	False	Correct	Correct	False	Correct	Correct	False	Correct	Correct	False	Correct	Correct	Correct	Correct	Correct	False	Correct	Correct	Correct	Correct	False	Correct	Correct	False	Correct	Correct	Correct	Correct	Correct	False	Correct	Correct	Correct	Correct	Correct	Correct	Correct	Correct	False