Art8-2024

Member State report / Art8-2024 / 2024 / D3 / Italy / Mediterranean: Adriatic 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: Adriatic Sea
Report date	2025-09-11 10:38:38

MAD-IT-MS-AS

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	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	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	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	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	Alloteuthis media	Alloteuthis media	Alloteuthis media	Alloteuthis media	Alloteuthis media	Alloteuthis media	Aristaeomorpha foliacea	Aristaeomorpha foliacea	Aristaeomorpha foliacea	Aristaeomorpha foliacea	Aristaeomorpha foliacea	Aristaeomorpha foliacea	Aristeus antennatus	Aristeus antennatus	Aristeus antennatus	Aristeus antennatus	Aristeus antennatus	Aristeus antennatus	Bolinus brandaris	Bolinus brandaris	Bolinus brandaris	Bolinus brandaris	Bolinus brandaris	Bolinus brandaris	Chamelea gallina	Chamelea gallina	Chamelea gallina	Chamelea gallina	Chamelea gallina	Chamelea gallina	Chelidonichthys lucerna	Chelidonichthys lucerna	Chelidonichthys lucerna	Chelidonichthys lucerna	Chelidonichthys lucerna	Chelidonichthys lucerna	Eledone cirrhosa	Eledone cirrhosa	Eledone cirrhosa	Eledone cirrhosa	Eledone cirrhosa	Eledone cirrhosa	Eledone moschata	Eledone moschata	Eledone moschata	Eledone moschata	Eledone moschata	Eledone moschata	Engraulis encrasicolus	Engraulis encrasicolus	Engraulis encrasicolus	Engraulis encrasicolus	Engraulis encrasicolus	Engraulis encrasicolus	Illex coindetii	Illex coindetii	Illex coindetii	Illex coindetii	Illex coindetii	Illex coindetii	Loligo vulgaris	Loligo vulgaris	Loligo vulgaris	Loligo vulgaris	Loligo vulgaris	Loligo vulgaris	Lophius budegassa	Lophius budegassa	Lophius budegassa	Lophius budegassa	Lophius budegassa	Lophius budegassa	Merlangius merlangus	Merlangius merlangus	Merlangius merlangus	Merlangius merlangus	Merlangius merlangus	Merlangius merlangus	Merluccius merluccius	Merluccius merluccius	Merluccius merluccius	Merluccius merluccius	Merluccius merluccius	Merluccius merluccius	Mullus barbatus	Mullus barbatus	Mullus barbatus	Mullus barbatus	Mullus barbatus	Mullus barbatus	Mullus surmuletus	Mullus surmuletus	Mullus surmuletus	Mullus surmuletus	Mullus surmuletus	Mullus surmuletus	Mustelus mustelus	Mustelus mustelus	Mustelus mustelus	Mustelus mustelus	Mustelus mustelus	Mustelus mustelus	Nephrops norvegicus	Nephrops norvegicus	Nephrops norvegicus	Nephrops norvegicus	Nephrops norvegicus	Nephrops norvegicus	Octopus vulgaris	Octopus vulgaris	Octopus vulgaris	Octopus vulgaris	Octopus vulgaris	Octopus vulgaris	Parapenaeus longirostris	Parapenaeus longirostris	Parapenaeus longirostris	Parapenaeus longirostris	Parapenaeus longirostris	Parapenaeus longirostris	Pecten jacobaeus	Pecten jacobaeus	Pecten jacobaeus	Pecten jacobaeus	Pecten jacobaeus	Pecten jacobaeus	Penaeus kerathurus	Penaeus kerathurus	Penaeus kerathurus	Penaeus kerathurus	Penaeus kerathurus	Penaeus kerathurus	Sardina pilchardus	Sardina pilchardus	Sardina pilchardus	Sardina pilchardus	Sardina pilchardus	Sardina pilchardus	Scophthalmus maximus	Scophthalmus maximus	Scophthalmus maximus	Scophthalmus maximus	Scophthalmus maximus	Scophthalmus maximus	Sepia officinalis	Sepia officinalis	Sepia officinalis	Sepia officinalis	Sepia officinalis	Sepia officinalis	Solea solea	Solea solea	Solea solea	Solea solea	Solea solea	Solea solea	Squilla mantis	Squilla mantis	Squilla mantis	Squilla mantis	Squilla mantis	Squilla mantis	Trachurus mediterraneus	Trachurus mediterraneus	Trachurus mediterraneus	Trachurus mediterraneus	Trachurus mediterraneus	Trachurus mediterraneus	Trachurus trachurus	Trachurus trachurus	Trachurus trachurus	Trachurus trachurus	Trachurus trachurus	Trachurus trachurus	Trisopterus minutus	Trisopterus minutus	Trisopterus minutus	Trisopterus minutus	Trisopterus minutus	Trisopterus minutus	Zeus faber	Zeus faber	Zeus faber	Zeus faber	Zeus faber	Zeus faber
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		Stable		Stable		Stable		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Stable		Stable		Stable		Stable		Stable		Stable		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Improving		Improving		Improving		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Stable		Stable		Stable		Unknown		Unknown		Unknown		Stable		Stable		Stable		Stable		Stable		Stable		Stable		Stable		Stable		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown
Element 2	Midsize squid (Alloteuthis media) in GSA 17-18 (Adriatic Sea)	Midsize squid (Alloteuthis media) in GSA 17-18 (Adriatic Sea)	Midsize squid (Alloteuthis media) in GSA 17-18 (Adriatic Sea)	Midsize squid (Alloteuthis media) in GSA 17-18 (Adriatic Sea)	Midsize squid (Alloteuthis media) in GSA 17-18 (Adriatic Sea)	Midsize squid (Alloteuthis media) in GSA 17-18 (Adriatic Sea)	Giant red shrimp (Aristaemorpha foliacea) in GSAs 18-19-20	Giant red shrimp (Aristaemorpha foliacea) in GSAs 18-19-20	Giant red shrimp (Aristaemorpha foliacea) in GSAs 18-19-20	Giant red shrimp (Aristaemorpha foliacea) in GSAs 18-19-20	Giant red shrimp (Aristaemorpha foliacea) in GSAs 18-19-20	Giant red shrimp (Aristaemorpha foliacea) in GSAs 18-19-20	Blue and red shrimp (Aristeus antennatus) in GSAs 18-19-20	Blue and red shrimp (Aristeus antennatus) in GSAs 18-19-20	Blue and red shrimp (Aristeus antennatus) in GSAs 18-19-20	Blue and red shrimp (Aristeus antennatus) in GSAs 18-19-20	Blue and red shrimp (Aristeus antennatus) in GSAs 18-19-20	Blue and red shrimp (Aristeus antennatus) in GSAs 18-19-20	Purple dye murex (Bolinus brandaris) in GSA 17 (Northern Adriatic Sea)	Purple dye murex (Bolinus brandaris) in GSA 17 (Northern Adriatic Sea)	Purple dye murex (Bolinus brandaris) in GSA 17 (Northern Adriatic Sea)	Purple dye murex (Bolinus brandaris) in GSA 17 (Northern Adriatic Sea)	Purple dye murex (Bolinus brandaris) in GSA 17 (Northern Adriatic Sea)	Purple dye murex (Bolinus brandaris) in GSA 17 (Northern Adriatic Sea)	Striped venus (Chamelea gallina) in GSA 17 (Northern Adriatic Sea)	Striped venus (Chamelea gallina) in GSA 17 (Northern Adriatic Sea)	Striped venus (Chamelea gallina) in GSA 17 (Northern Adriatic Sea)	Striped venus (Chamelea gallina) in GSA 17 (Northern Adriatic Sea)	Striped venus (Chamelea gallina) in GSA 17 (Northern Adriatic Sea)	Striped venus (Chamelea gallina) in GSA 17 (Northern Adriatic Sea)	Tub gurnard (Chelidonichthys lucerna) in GSA 17 (Northern Adriatic Sea)	Tub gurnard (Chelidonichthys lucerna) in GSA 17 (Northern Adriatic Sea)	Tub gurnard (Chelidonichthys lucerna) in GSA 17 (Northern Adriatic Sea)	Tub gurnard (Chelidonichthys lucerna) in GSA 17 (Northern Adriatic Sea)	Tub gurnard (Chelidonichthys lucerna) in GSA 17 (Northern Adriatic Sea)	Tub gurnard (Chelidonichthys lucerna) in GSA 17 (Northern Adriatic Sea)	Horned octopus (Eledone cirrhosa) in GSA 18 (Southern Adriatic Sea)	Horned octopus (Eledone cirrhosa) in GSA 18 (Southern Adriatic Sea)	Horned octopus (Eledone cirrhosa) in GSA 18 (Southern Adriatic Sea)	Horned octopus (Eledone cirrhosa) in GSA 18 (Southern Adriatic Sea)	Horned octopus (Eledone cirrhosa) in GSA 18 (Southern Adriatic Sea)	Horned octopus (Eledone cirrhosa) in GSA 18 (Southern Adriatic Sea)	Musky octopus (Eledone moschata) in GSA 17-18 (Adriatic Sea)	Musky octopus (Eledone moschata) in GSA 17-18 (Adriatic Sea)	Musky octopus (Eledone moschata) in GSA 17-18 (Adriatic Sea)	Musky octopus (Eledone moschata) in GSA 17-18 (Adriatic Sea)	Musky octopus (Eledone moschata) in GSA 17-18 (Adriatic Sea)	Musky octopus (Eledone moschata) in GSA 17-18 (Adriatic Sea)	Anchovy (Engraulis encrasicolus) in GSA 17-18 (Adriatic Sea)	Anchovy (Engraulis encrasicolus) in GSA 17-18 (Adriatic Sea)	Anchovy (Engraulis encrasicolus) in GSA 17-18 (Adriatic Sea)	Anchovy (Engraulis encrasicolus) in GSA 17-18 (Adriatic Sea)	Anchovy (Engraulis encrasicolus) in GSA 17-18 (Adriatic Sea)	Anchovy (Engraulis encrasicolus) in GSA 17-18 (Adriatic Sea)	Broadtail shortfin squid (Illex coindetii) in GSA 17-18 (Adriatic Sea)	Broadtail shortfin squid (Illex coindetii) in GSA 17-18 (Adriatic Sea)	Broadtail shortfin squid (Illex coindetii) in GSA 17-18 (Adriatic Sea)	Broadtail shortfin squid (Illex coindetii) in GSA 17-18 (Adriatic Sea)	Broadtail shortfin squid (Illex coindetii) in GSA 17-18 (Adriatic Sea)	Broadtail shortfin squid (Illex coindetii) in GSA 17-18 (Adriatic Sea)	European squid (Loligo vulgaris) in GSA 17-18 (Adriatic Sea)	European squid (Loligo vulgaris) in GSA 17-18 (Adriatic Sea)	European squid (Loligo vulgaris) in GSA 17-18 (Adriatic Sea)	European squid (Loligo vulgaris) in GSA 17-18 (Adriatic Sea)	European squid (Loligo vulgaris) in GSA 17-18 (Adriatic Sea)	European squid (Loligo vulgaris) in GSA 17-18 (Adriatic Sea)	Black-bellied anglerfish (Lophius budegassa) in GSA 17 (Northern Adriatic Sea)	Black-bellied anglerfish (Lophius budegassa) in GSA 17 (Northern Adriatic Sea)	Black-bellied anglerfish (Lophius budegassa) in GSA 17 (Northern Adriatic Sea)	Black-bellied anglerfish (Lophius budegassa) in GSA 17 (Northern Adriatic Sea)	Black-bellied anglerfish (Lophius budegassa) in GSA 17 (Northern Adriatic Sea)	Black-bellied anglerfish (Lophius budegassa) in GSA 17 (Northern Adriatic Sea)	Whiting (Merlangius merlangus) in GSA 17-18 (Adriatic Sea)	Whiting (Merlangius merlangus) in GSA 17-18 (Adriatic Sea)	Whiting (Merlangius merlangus) in GSA 17-18 (Adriatic Sea)	Whiting (Merlangius merlangus) in GSA 17-18 (Adriatic Sea)	Whiting (Merlangius merlangus) in GSA 17-18 (Adriatic Sea)	Whiting (Merlangius merlangus) in GSA 17-18 (Adriatic Sea)	European hake (Merluccius merluccius) in GSA 17-18 (Adriatic Sea)	European hake (Merluccius merluccius) in GSA 17-18 (Adriatic Sea)	European hake (Merluccius merluccius) in GSA 17-18 (Adriatic Sea)	European hake (Merluccius merluccius) in GSA 17-18 (Adriatic Sea)	European hake (Merluccius merluccius) in GSA 17-18 (Adriatic Sea)	European hake (Merluccius merluccius) in GSA 17-18 (Adriatic Sea)	Red mullet (Mullus barbatus) in GSA 17-18 (Adriatic Sea)	Red mullet (Mullus barbatus) in GSA 17-18 (Adriatic Sea)	Red mullet (Mullus barbatus) in GSA 17-18 (Adriatic Sea)	Red mullet (Mullus barbatus) in GSA 17-18 (Adriatic Sea)	Red mullet (Mullus barbatus) in GSA 17-18 (Adriatic Sea)	Red mullet (Mullus barbatus) in GSA 17-18 (Adriatic Sea)	Striped red mullet (Mullus surmuletus) in GSA 17-18 (Adriatic Sea)	Striped red mullet (Mullus surmuletus) in GSA 17-18 (Adriatic Sea)	Striped red mullet (Mullus surmuletus) in GSA 17-18 (Adriatic Sea)	Striped red mullet (Mullus surmuletus) in GSA 17-18 (Adriatic Sea)	Striped red mullet (Mullus surmuletus) in GSA 17-18 (Adriatic Sea)	Striped red mullet (Mullus surmuletus) in GSA 17-18 (Adriatic Sea)	Smooth-hound (Mustelus mustelus) in GSA 17-18 (Adriatic Sea)	Smooth-hound (Mustelus mustelus) in GSA 17-18 (Adriatic Sea)	Smooth-hound (Mustelus mustelus) in GSA 17-18 (Adriatic Sea)	Smooth-hound (Mustelus mustelus) in GSA 17-18 (Adriatic Sea)	Smooth-hound (Mustelus mustelus) in GSA 17-18 (Adriatic Sea)	Smooth-hound (Mustelus mustelus) in GSA 17-18 (Adriatic Sea)	Norway lobster (Nephrops norvegicus) in GSA 17-18 (Adriatic Sea)	Norway lobster (Nephrops norvegicus) in GSA 17-18 (Adriatic Sea)	Norway lobster (Nephrops norvegicus) in GSA 17-18 (Adriatic Sea)	Norway lobster (Nephrops norvegicus) in GSA 17-18 (Adriatic Sea)	Norway lobster (Nephrops norvegicus) in GSA 17-18 (Adriatic Sea)	Norway lobster (Nephrops norvegicus) in GSA 17-18 (Adriatic Sea)	Common octopus (Octopus vulgaris) in GSA 17-18 (Adriatic Sea)	Common octopus (Octopus vulgaris) in GSA 17-18 (Adriatic Sea)	Common octopus (Octopus vulgaris) in GSA 17-18 (Adriatic Sea)	Common octopus (Octopus vulgaris) in GSA 17-18 (Adriatic Sea)	Common octopus (Octopus vulgaris) in GSA 17-18 (Adriatic Sea)	Common octopus (Octopus vulgaris) in GSA 17-18 (Adriatic Sea)	Deep-water rose shrimp (Parapenaeus longirostris) in GSAs 17-18-19	Deep-water rose shrimp (Parapenaeus longirostris) in GSAs 17-18-19	Deep-water rose shrimp (Parapenaeus longirostris) in GSAs 17-18-19	Deep-water rose shrimp (Parapenaeus longirostris) in GSAs 17-18-19	Deep-water rose shrimp (Parapenaeus longirostris) in GSAs 17-18-19	Deep-water rose shrimp (Parapenaeus longirostris) in GSAs 17-18-19	Great Mediterranean scallop (Pecten jacobaeus) in GSA 17 (Northern Adriatic Sea)	Great Mediterranean scallop (Pecten jacobaeus) in GSA 17 (Northern Adriatic Sea)	Great Mediterranean scallop (Pecten jacobaeus) in GSA 17 (Northern Adriatic Sea)	Great Mediterranean scallop (Pecten jacobaeus) in GSA 17 (Northern Adriatic Sea)	Great Mediterranean scallop (Pecten jacobaeus) in GSA 17 (Northern Adriatic Sea)	Great Mediterranean scallop (Pecten jacobaeus) in GSA 17 (Northern Adriatic Sea)	Caramote prawn (Penaeus kerathurus) in GSA 17 (Northern Adriatic Sea)	Caramote prawn (Penaeus kerathurus) in GSA 17 (Northern Adriatic Sea)	Caramote prawn (Penaeus kerathurus) in GSA 17 (Northern Adriatic Sea)	Caramote prawn (Penaeus kerathurus) in GSA 17 (Northern Adriatic Sea)	Caramote prawn (Penaeus kerathurus) in GSA 17 (Northern Adriatic Sea)	Caramote prawn (Penaeus kerathurus) in GSA 17 (Northern Adriatic Sea)	Sardine (Sardina Pilchardus) in GSA 17-18 (Adriatic Sea)	Sardine (Sardina Pilchardus) in GSA 17-18 (Adriatic Sea)	Sardine (Sardina Pilchardus) in GSA 17-18 (Adriatic Sea)	Sardine (Sardina Pilchardus) in GSA 17-18 (Adriatic Sea)	Sardine (Sardina Pilchardus) in GSA 17-18 (Adriatic Sea)	Sardine (Sardina Pilchardus) in GSA 17-18 (Adriatic Sea)	Turbot (Scophthalmus maximus) in GSA 17 (Northern Adriatic Sea)	Turbot (Scophthalmus maximus) in GSA 17 (Northern Adriatic Sea)	Turbot (Scophthalmus maximus) in GSA 17 (Northern Adriatic Sea)	Turbot (Scophthalmus maximus) in GSA 17 (Northern Adriatic Sea)	Turbot (Scophthalmus maximus) in GSA 17 (Northern Adriatic Sea)	Turbot (Scophthalmus maximus) in GSA 17 (Northern Adriatic Sea)	Common cuttlefish (Sepia officinalis) in GSA 17 (Adriatic Sea)	Common cuttlefish (Sepia officinalis) in GSA 17 (Adriatic Sea)	Common cuttlefish (Sepia officinalis) in GSA 17 (Adriatic Sea)	Common cuttlefish (Sepia officinalis) in GSA 17 (Adriatic Sea)	Common cuttlefish (Sepia officinalis) in GSA 17 (Adriatic Sea)	Common cuttlefish (Sepia officinalis) in GSA 17 (Adriatic Sea)	Sole (Solea solea) in GSA 17 (Northern Adriatic Sea)	Sole (Solea solea) in GSA 17 (Northern Adriatic Sea)	Sole (Solea solea) in GSA 17 (Northern Adriatic Sea)	Sole (Solea solea) in GSA 17 (Northern Adriatic Sea)	Sole (Solea solea) in GSA 17 (Northern Adriatic Sea)	Sole (Solea solea) in GSA 17 (Northern Adriatic Sea)	Spottail mantis squillid (Squilla mantis) in GSA 17 (Northern Adriatic Sea)	Spottail mantis squillid (Squilla mantis) in GSA 17 (Northern Adriatic Sea)	Spottail mantis squillid (Squilla mantis) in GSA 17 (Northern Adriatic Sea)	Spottail mantis squillid (Squilla mantis) in GSA 17 (Northern Adriatic Sea)	Spottail mantis squillid (Squilla mantis) in GSA 17 (Northern Adriatic Sea)	Spottail mantis squillid (Squilla mantis) in GSA 17 (Northern Adriatic Sea)	Mediterranean horse mackerel (Trachurus mediterraneus) in GSA 17 (Northern Adriatic Sea)	Mediterranean horse mackerel (Trachurus mediterraneus) in GSA 17 (Northern Adriatic Sea)	Mediterranean horse mackerel (Trachurus mediterraneus) in GSA 17 (Northern Adriatic Sea)	Mediterranean horse mackerel (Trachurus mediterraneus) in GSA 17 (Northern Adriatic Sea)	Mediterranean horse mackerel (Trachurus mediterraneus) in GSA 17 (Northern Adriatic Sea)	Mediterranean horse mackerel (Trachurus mediterraneus) in GSA 17 (Northern Adriatic Sea)	Atlantic horse mackerel (Trachurus trachurus) in GSA 17 (Northern Adriatic Sea)	Atlantic horse mackerel (Trachurus trachurus) in GSA 17 (Northern Adriatic Sea)	Atlantic horse mackerel (Trachurus trachurus) in GSA 17 (Northern Adriatic Sea)	Atlantic horse mackerel (Trachurus trachurus) in GSA 17 (Northern Adriatic Sea)	Atlantic horse mackerel (Trachurus trachurus) in GSA 17 (Northern Adriatic Sea)	Atlantic horse mackerel (Trachurus trachurus) in GSA 17 (Northern Adriatic Sea)	Poor cod (Trisopterus minutus) in GSA 17-18 (Adriatic Sea)	Poor cod (Trisopterus minutus) in GSA 17-18 (Adriatic Sea)	Poor cod (Trisopterus minutus) in GSA 17-18 (Adriatic Sea)	Poor cod (Trisopterus minutus) in GSA 17-18 (Adriatic Sea)	Poor cod (Trisopterus minutus) in GSA 17-18 (Adriatic Sea)	Poor cod (Trisopterus minutus) in GSA 17-18 (Adriatic Sea)	John dory (Zeus faber) in GSAs 17-18	John dory (Zeus faber) in GSAs 17-18	John dory (Zeus faber) in GSAs 17-18	John dory (Zeus faber) in GSAs 17-18	John dory (Zeus faber) in GSAs 17-18	John dory (Zeus faber) in GSAs 17-18
Element source		National		National		National		National		National		National		National		National		National		National		National		National		STECF		STECF		STECF		National		National		National		GFCM		GFCM		GFCM		National		National		National		GFCM		GFCM		GFCM		National		National		National		National		National		National		GFCM		GFCM		GFCM		National		National		National		STECF		STECF		STECF		STECF		STECF		STECF		National		National		National		National		National		National		STECF		STECF		STECF		National		National		National		STECF		STECF		STECF		National		National		National		GFCM		GFCM		GFCM		GFCM		GFCM		GFCM		National		National		National		GFCM		GFCM		GFCM		STECF		STECF		STECF		GFCM		GFCM		GFCM		National		National		National		National		National		National		National		National		National		National		National		National
Criterion	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3	D3C1	D3C1	D3C2	D3C2	D3C3	D3C3
Parameter		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref		Fcurr/Fref		SSBcurr/SSBref		L90/L90ref
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		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		National		National		National		National		National		National		National		National		National		National		National		National		Common Fisheries Policy		Common Fisheries Policy		National		National		National		National		Common Fisheries Policy		Common Fisheries Policy		National		National		National		National		Common Fisheries Policy		Common Fisheries Policy		National		National		National		National		National		National		National		Common Fisheries Policy		Common Fisheries Policy		National		National		National		National		Common Fisheries Policy		Common Fisheries Policy		National		Common Fisheries Policy		Common Fisheries Policy		National		National		National		National		National		National		National		Common Fisheries Policy		Common Fisheries Policy		National		National		National		National		Common Fisheries Policy		Common Fisheries Policy		National		National		National		National		Common Fisheries Policy		Common Fisheries Policy		National		Common Fisheries Policy		Common Fisheries Policy		National		National		National		National		Common Fisheries Policy		Common Fisheries Policy		National		Common Fisheries Policy		Common Fisheries Policy		National		Common Fisheries Policy		Common Fisheries Policy		National		National		National		National		National		National		National		National		National		National		National		National		National
Value achieved upper		1.08		0.98				2.78						2.91						0.86		2.92				1.03						1.08		4.46		0.99		1.0		1.03		0.89		0.99		1.06		1.05		1.03		1.16				1.03		3.95		0.9		0.81		1.07		1.07		1.23		0.91		1.11		1.21		0.93				2.46		1.08		0.95		0.32		1.71		0.94		0.82		0.36				0.45		1.39		1.02		0.88		1.27		1.02		0.63		1.85		1.2		1.78						3.75		0.05				1.23		1.3		0.82		1.47		0.87				1.65		0.39				1.37		0.29				1.14		0.75		0.95		1.07		8.96		0.99		0.62		0.62				0.62		0.62				1.74		0.44				0.47		0.26		1.0
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
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		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		% 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		Improving		Deteriorating		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Deteriorating		Improving		Unknown		Improving		Deteriorating		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Improving		Improving		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Improving		Deteriorating		Unknown		Unknown		Unknown		Unknown		Improving		Deteriorating		Unknown		Improving		Improving		Unknown		Improving		Improving		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown		Unknown
Parameter achieved		No		No		Unknown		No		Unknown		Unknown		No		Unknown		Unknown		Yes		Yes		Unknown		No		Unknown		Unknown		No		Yes		Unknown		Yes		Yes		Unknown		Yes		Yes		Unknown		No		Yes		Unknown		Yes		Yes		Unknown		Yes		Yes		Unknown		No		No		Unknown		No		No		Unknown		No		Yes		Unknown		Yes		Yes		Unknown		Yes		No		Unknown		Yes		Yes		Unknown		Yes		Yes		Unknown		Yes		Yes		Unknown		No		Unknown		Unknown		No		No		Unknown		No		Yes		Unknown		No		No		Unknown		No		No		Unknown		No		No		Unknown		No		No		Unknown		No		Yes		Unknown		Yes		No		Unknown		Yes		No		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.		For the subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref		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 subregion MAD, 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 L90ref, which represents the reference values estimated from sustainably exploited simulated populations (when available) or the average L90 during years when the stock was sustainably fished, defined as F < Fmsy. This method was used only if the number of years in which F < Fmsy constituted at least 40% of the historical series. In both cases, the average was calculated from 2016 to 2021. This parameter is denoted as L90/L90ref
Related indicator		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3		MAD-IT-MS-AS-D3
Criteria status	Not good	Not good	Not good	Not good	Unknown	Unknown	Not good	Not good	Unknown	Unknown	Unknown	Unknown	Not good	Not good	Unknown	Unknown	Unknown	Unknown	Good	Good	Good	Good	Unknown	Unknown	Not good	Not good	Unknown	Unknown	Unknown	Unknown	Not good	Not good	Good	Good	Unknown	Unknown	Good	Good	Good	Good	Unknown	Unknown	Good	Good	Good	Good	Unknown	Unknown	Not good	Not good	Good	Good	Unknown	Unknown	Not good	Not good	Good	Good	Unknown	Unknown	Good	Good	Good	Good	Unknown	Unknown	Not good	Not good	Not good	Not good	Unknown	Unknown	Not good	Not good	Not good	Not good	Unknown	Unknown	Not good	Not good	Good	Good	Unknown	Unknown	Good	Good	Good	Good	Unknown	Unknown	Good	Good	Not good	Not good	Unknown	Unknown	Good	Good	Good	Good	Unknown	Unknown	Good	Good	Good	Good	Unknown	Unknown	Good	Good	Good	Good	Unknown	Unknown	Not good	Not good	Unknown	Unknown	Unknown	Unknown	Not good	Not good	Not good	Not good	Unknown	Unknown	Not good	Not good	Good	Good	Unknown	Unknown	Not good	Not good	Not good	Not good	Unknown	Unknown	Not good	Not good	Not good	Not good	Unknown	Unknown	Not good	Not good	Not good	Not good	Unknown	Unknown	Not good	Not good	Not good	Not good	Unknown	Unknown	Not good	Not good	Good	Good	Unknown	Unknown	Good	Good	Not good	Not good	Unknown	Unknown	Good	Good	Not good	Not good	Unknown	Unknown	Not good	Not good	Not good	Not good	Unknown	Unknown	Good	Good	Not good	Not good	Unknown	Unknown
Description criteria	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).	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 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 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 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 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 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 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 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 D3C1. 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 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 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 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 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).	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 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 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 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 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 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).	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 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 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 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).	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 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 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 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).	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 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 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 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).	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 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 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 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 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 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 D3C1. 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 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 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 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 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).	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 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).	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 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 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 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).	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 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).	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 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 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 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 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 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).	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 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 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 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		Good		Good		Good		Not good		Not good		Not good		Not good		Not good		Not good		Good		Good		Good		Good		Good		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		Good		Good		Good		Not good		Not good		Not good		Good		Good		Good		Good		Good		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		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		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		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		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		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		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		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		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)		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		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		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		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		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)		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		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005		MAD-IT-D03-T001 MAD-IT-D03-T002 MAD-IT-D03-T003 MAD-IT-D03-T004 MAD-IT-D03-T005
Test TV	NA	No	NA	No	NA	NA	NA	No	NA	NA	NA	NA	NA	No	NA	NA	NA	NA	NA	Yes	NA	Yes	NA	NA	NA	No	NA	NA	NA	NA	NA	No	NA	Yes	NA	No	NA	Yes	NA	Yes	NA	No	NA	Yes	NA	Yes	NA	Yes	NA	No	NA	Yes	NA	NA	NA	No	NA	Yes	NA	No	NA	Yes	NA	Yes	NA	Yes	NA	No	NA	No	NA	Yes	NA	No	NA	No	NA	NA	NA	No	NA	Yes	NA	No	NA	Yes	NA	Yes	NA	No	NA	Yes	NA	No	NA	NA	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	Yes	NA	No	NA	NA	NA	NA	NA	No	NA	No	NA	NA	NA	No	NA	Yes	NA	No	NA	No	NA	No	NA	NA	NA	No	NA	No	NA	NA	NA	No	NA	No	NA	NA	NA	No	NA	No	NA	No	NA	No	NA	Yes	NA	No	NA	Yes	NA	No	NA	NA	NA	Yes	NA	No	NA	NA	NA	No	NA	No	NA	NA	NA	Yes	NA	No	NA	No
Test results	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	False	False	Correct	False	Correct	False	False	False	Correct	False	Correct	False	False	False	Correct	False	Correct	False	Correct	False	False	False	Correct	False	False	False	Correct	False	Correct	False	False	False	Correct	False	Correct	False	False	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	False	False	Correct	False	Correct	False	False	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	False	False	Correct	False	Correct	False	False	False	Correct	False	Correct	False	False	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	False	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	False	False	Correct	False	Correct	False	False	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	Correct	False	False

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	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	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish
Element	Aristaeomorpha foliacea	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	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	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
Element 2	Giant red shrimp (Aristaemorpha foliacea) in GSA 16 (Southern Sicily)	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 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 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
Criterion	D3C3	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	D3C3	D3C1	D3C2	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	D3C1	D3C2	D3C3	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
Threshold value upper
Threshold value lower
Threshold value operator
Threshold qualitative
Threshold value source
Value achieved upper
Value achieved lower
Value unit
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend parameter
Parameter achieved
Description parameter
Related indicator
Criteria status	Unknown	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	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	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
Description element
Source assessment feature
Reporting method feature
Trend feature
Integration rule type parameter
Integration rule description parameter
Integration rule type criteria
Integration rule description criteria
GES extent threshold
GES extent achieved
GES extent unit
GES achieved
Description overall status
Assessments period
Related pressures
Related targets
Test TV	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA
Test results	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False

MWE-IT-MS-WMS

Simplified table

Regional assessment area
Component MRUs
GES component	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3	D3
Feature	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish	Commercially exploited fish and shellfish
Element	Aristaeomorpha foliacea	Aristaeomorpha foliacea	Aristaeomorpha foliacea	Aristeus antennatus	Aristeus antennatus	Aristeus antennatus	Boops boops	Boops boops	Boops boops	Eledone cirrhosa	Eledone cirrhosa	Eledone cirrhosa	Engraulis encrasicolus	Engraulis encrasicolus	Engraulis encrasicolus	Helicolenus dactylopterus	Helicolenus dactylopterus	Helicolenus dactylopterus	Illex coindetii	Illex coindetii	Illex coindetii	Lophius budegassa	Lophius budegassa	Lophius budegassa	Merluccius merluccius	Merluccius merluccius	Merluccius merluccius	Micromesistius poutassou	Micromesistius poutassou	Micromesistius poutassou	Mullus barbatus	Mullus barbatus	Mullus barbatus	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 bogaraveo	Pagellus bogaraveo	Pagellus bogaraveo	Pagellus erythrinus	Pagellus erythrinus	Pagellus erythrinus	Parapenaeus longirostris	Parapenaeus longirostris	Parapenaeus longirostris	Phycis blennoides	Phycis blennoides	Phycis blennoides	Raja asterias	Raja asterias	Raja asterias	Raja clavata	Raja clavata	Raja clavata	Sardina pilchardus	Sardina pilchardus	Sardina pilchardus	Scyliorhinus canicula	Scyliorhinus canicula	Scyliorhinus canicula	Trachurus mediterraneus	Trachurus mediterraneus	Trachurus mediterraneus	Trachurus trachurus	Trachurus trachurus	Trachurus trachurus	Trisopterus minutus	Trisopterus minutus	Trisopterus minutus	Zeus faber	Zeus faber	Zeus faber
Element extent
Trend element
Element 2	Giant red shrimp (Aristaemorpha foliacea) in GSAs 9-10-11	Giant red shrimp (Aristaemorpha foliacea) in GSAs 9-10-11	Giant red shrimp (Aristaemorpha foliacea) in GSAs 9-10-11	Blue and red shrimp (Aristeus antennatus) in GSAs 9-10-11	Blue and red shrimp (Aristeus antennatus) in GSAs 9-10-11	Blue and red shrimp (Aristeus antennatus) in GSAs 9-10-11	Bogue (Boops boops) in GSAs 8-9-10-11	Bogue (Boops boops) in GSAs 8-9-10-11	Bogue (Boops boops) in GSAs 8-9-10-11	Horned octopus (Eledone cirrhosa) in GSAs 8-9-10-11	Horned octopus (Eledone cirrhosa) in GSAs 8-9-10-11	Horned octopus (Eledone cirrhosa) in GSAs 8-9-10-11	Anchovy (Engraulis encrasicolus) in GSA 9 (Ligurian Sea and Northern Tyrrhenian Sea)	Anchovy (Engraulis encrasicolus) in GSA 9 (Ligurian Sea and Northern Tyrrhenian Sea)	Anchovy (Engraulis encrasicolus) in GSA 9 (Ligurian Sea and Northern Tyrrhenian Sea)	Blackbelly rosefish (Helicolenus dactylopterus) in GSAs 8-9-10-11	Blackbelly rosefish (Helicolenus dactylopterus) in GSAs 8-9-10-11	Blackbelly rosefish (Helicolenus dactylopterus) in GSAs 8-9-10-11	Broadtail shortfin squid (Illex coindetii) in GSAs 8-9-10-11	Broadtail shortfin squid (Illex coindetii) in GSAs 8-9-10-11	Broadtail shortfin squid (Illex coindetii) in GSAs 8-9-10-11	Black-bellied anglerfish (Lophius budegassa) in GSAs 8-9-10-11	Black-bellied anglerfish (Lophius budegassa) in GSAs 8-9-10-11	Black-bellied anglerfish (Lophius budegassa) in GSAs 8-9-10-11	European hake (Merluccius merluccius) in GSAs 8-9-10-11	European hake (Merluccius merluccius) in GSAs 8-9-10-11	European hake (Merluccius merluccius) in GSAs 9-10-11	Blue whiting (Micromesistius poutassou) in GSAs 8-9-10-11	Blue whiting (Micromesistius poutassou) in GSAs 8-9-10-11	Blue whiting (Micromesistius poutassou) in GSAs 8-9-10-11	Red mullet (Mullus barbatus) in GSA 10 (Southern and Central Tyrrhenian Sea)	Red mullet (Mullus barbatus) in GSA 10 (Southern and Central Tyrrhenian Sea)	Red mullet (Mullus barbatus) in GSA 10 (Southern and Central Tyrrhenian Sea)	Red mullet (Mullus barbatus) in GSA 9 (Ligurian Sea and North Tyrrhenian Sea)	Red mullet (Mullus barbatus) in GSA 9 (Ligurian Sea and North Tyrrhenian Sea)	Red mullet (Mullus barbatus) in GSAs 9-10-11	Striped red mullet (Mullus surmuletus) in GSAs 8-9-10-11	Striped red mullet (Mullus surmuletus) in GSAs 8-9-10-11	Striped red mullet (Mullus surmuletus) in GSAs 8-9-10-11	Norway lobster (Nephrops norvegicus) in GSA 9 (Ligurian Sea and North Tyrrhenian Sea)	Norway lobster (Nephrops norvegicus) in GSA 9 (Ligurian Sea and North Tyrrhenian Sea)	Norway lobster (Nephrops norvegicus) in GSA 9 (Ligurian Sea and North Tyrrhenian Sea)	Common octopus (Octopus vulgaris) in GSAs 8-9-10-11	Common octopus (Octopus vulgaris) in GSAs 8-9-10-11	Common octopus (Octopus vulgaris) in GSAs 8-9-10-11	Blackspot seabream (Pagellus bogaraveo) in GSAs 8-9-10-11	Blackspot seabream (Pagellus bogaraveo) in GSAs 8-9-10-11	Blackspot seabream (Pagellus bogaraveo) in GSAs 8-9-10-11	Common pandora (Pagellus erythrinus) in GSAs 8-9-10-11	Common pandora (Pagellus erythrinus) in GSAs 8-9-10-11	Common pandora (Pagellus erythrinus) in GSAs 8-9-10-11	Deep-water rose shrimp (Parapenaeus longirostris) in GSAs 8-9-10-11	Deep-water rose shrimp (Parapenaeus longirostris) in GSAs 8-9-10-11	Deep-water rose shrimp (Parapenaeus longirostris) in GSAs 9-10-11	Greater forkbeard (Phycis blennoides) in GSAs 8-9-10-11	Greater forkbeard (Phycis blennoides) in GSAs 8-9-10-11	Greater forkbeard (Phycis blennoides) in GSAs 8-9-10-11	Mediterranean starry ray (Raja asterias) in GSAs 8-9-10-11	Mediterranean starry ray (Raja asterias) in GSAs 8-9-10-11	Mediterranean starry ray (Raja asterias) in GSAs 8-9-10-11	Thornback ray (Raja clavata) in GSAs 8-9-10-11	Thornback ray (Raja clavata) in GSAs 8-9-10-11	Thornback ray (Raja clavata) in GSAs 8-9-10-11	Sardine (Sardina Pilchardus) in GSA 9 (Ligurian Sea and North Tyrrhenian Sea)	Sardine (Sardina Pilchardus) in GSA 9 (Ligurian Sea and North Tyrrhenian Sea)	Sardine (Sardina Pilchardus) in GSA 9 (Ligurian Sea and North Tyrrhenian Sea)	Lesser-spotted dogfish (Scyliorhinus canicula) in GSAs 8-9-10-11	Lesser-spotted dogfish (Scyliorhinus canicula) in GSAs 8-9-10-11	Lesser-spotted dogfish (Scyliorhinus canicula) in GSAs 8-9-10-11	Mediterranean horse mackerel (Trachurus mediterraneus) in GSAs 8-9-10-11	Mediterranean horse mackerel (Trachurus mediterraneus) in GSAs 8-9-10-11	Mediterranean horse mackerel (Trachurus mediterraneus) in GSAs 8-9-10-11	Atlantic horse mackerel (Trachurus trachurus) in GSAs 8-9-10-11	Atlantic horse mackerel (Trachurus trachurus) in GSAs 8-9-10-11	Atlantic horse mackerel (Trachurus trachurus) in GSAs 8-9-10-11	Poor cod (Trisopterus minutus) in GSAs 8-9-10-11	Poor cod (Trisopterus minutus) in GSAs 8-9-10-11	Poor cod (Trisopterus minutus) in GSAs 8-9-10-11	John dory (Zeus faber) in GSAs 8-9-10-11	John dory (Zeus faber) in GSAs 8-9-10-11	John dory (Zeus faber) in GSAs 8-9-10-11
Element source
Criterion	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	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	D3C3
Parameter
Threshold value upper
Threshold value lower
Threshold value operator
Threshold qualitative
Threshold value source
Value achieved upper
Value achieved lower
Value unit
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend parameter
Parameter achieved
Description parameter
Related indicator
Criteria status	Not good	Not good	Unknown	Not good	Unknown	Unknown	Good	Good	Unknown	Not good	Not good	Unknown	Good	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	Good	Good	Unknown	Not good	Not good	Unknown	Not good	Not good	Unknown	Not good	Not good	Unknown	Not good	Not good	Unknown	Good	Good	Unknown	Good	Good	Unknown	Good	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	Good	Good	Unknown	Good	Good	Unknown	Not good	Not good	Unknown	Good	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).		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.).		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).		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).		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).	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.).		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.).		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.).		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.).
Element status
Description element
Source assessment feature
Reporting method feature
Trend feature
Integration rule type parameter
Integration rule description parameter
Integration rule type criteria
Integration rule description criteria
GES extent threshold
GES extent achieved
GES extent unit
GES achieved
Description overall status
Assessments period
Related pressures
Related targets
Test TV	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA	NA
Test results	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False	False