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

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
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
Element
Alloteuthis media
Alloteuthis media
Alloteuthis media
Aristaeomorpha foliacea
Aristaeomorpha foliacea
Aristaeomorpha foliacea
Aristeus antennatus
Aristeus antennatus
Aristeus antennatus
Bolinus brandaris
Bolinus brandaris
Bolinus brandaris
Chamelea gallina
Chamelea gallina
Chamelea gallina
Chelidonichthys lucerna
Chelidonichthys lucerna
Chelidonichthys lucerna
Eledone cirrhosa
Eledone cirrhosa
Eledone cirrhosa
Eledone moschata
Eledone moschata
Eledone moschata
Engraulis encrasicolus
Engraulis encrasicolus
Engraulis encrasicolus
Illex coindetii
Illex coindetii
Illex coindetii
Loligo vulgaris
Loligo vulgaris
Loligo vulgaris
Lophius budegassa
Lophius budegassa
Lophius budegassa
Merlangius merlangus
Merlangius merlangus
Merlangius merlangus
Merluccius merluccius
Merluccius merluccius
Merluccius merluccius
Mullus barbatus
Mullus barbatus
Mullus barbatus
Mullus surmuletus
Mullus surmuletus
Mullus surmuletus
Mustelus mustelus
Mustelus mustelus
Mustelus mustelus
Nephrops norvegicus
Nephrops norvegicus
Nephrops norvegicus
Octopus vulgaris
Octopus vulgaris
Octopus vulgaris
Parapenaeus longirostris
Parapenaeus longirostris
Parapenaeus longirostris
Pecten jacobaeus
Pecten jacobaeus
Pecten jacobaeus
Penaeus kerathurus
Penaeus kerathurus
Penaeus kerathurus
Sardina pilchardus
Sardina pilchardus
Sardina pilchardus
Scophthalmus maximus
Scophthalmus maximus
Scophthalmus maximus
Sepia officinalis
Sepia officinalis
Sepia officinalis
Solea solea
Solea solea
Solea solea
Squilla mantis
Squilla mantis
Squilla mantis
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
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)
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
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)
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)
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)
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)
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)
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)
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)
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)
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)
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)
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)
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)
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)
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
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
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
D3C1
D3C2
D3C3
D3C1
D3C2
D3C3
D3C1
D3C2
D3C3
D3C1
D3C2
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
Unknown
Not good
Unknown
Unknown
Not good
Unknown
Unknown
Good
Good
Unknown
Not good
Unknown
Unknown
Not good
Good
Unknown
Good
Good
Unknown
Good
Good
Unknown
Not good
Good
Unknown
Not good
Good
Unknown
Good
Good
Unknown
Not good
Not good
Unknown
Not good
Not good
Unknown
Not good
Good
Unknown
Good
Good
Unknown
Good
Not good
Unknown
Good
Good
Unknown
Good
Good
Unknown
Good
Good
Unknown
Not good
Unknown
Unknown
Not good
Not good
Unknown
Not good
Good
Unknown
Not good
Not good
Unknown
Not good
Not good
Unknown
Not good
Not good
Unknown
Not good
Not good
Unknown
Not good
Good
Unknown
Good
Not good
Unknown
Good
Not good
Unknown
Not good
Not good
Unknown
Good
Not good
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).
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).
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).
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).
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).
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.).
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).
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.).
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.).
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 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).
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).
Medium confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).
Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).
Medium confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).
Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).
Low confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods relying only on fisheries-independent data (AMSY).
Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).
Medium confidence level in the stock status according to criterion D3C1. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).
Medium confidence level in the stock status according to criterion D3C2. The parameter used to assess the stock status was based on the outcomes of assessments performed using “data-limited” methods based either on fisheries-independent data only (AMSY) or on both fisheries-dependent and fisheries-independent data (CMSY, BSM, SPiCT, etc.).
Element status
Not good
Not good
Not good
Not good
Not good
Not good
Not good
Not good
Not good
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
No
No
NA
No
NA
NA
No
NA
NA
Yes
Yes
NA
No
NA
NA
No
Yes
No
Yes
Yes
No
Yes
Yes
Yes
No
Yes
NA
No
Yes
No
Yes
Yes
Yes
No
No
Yes
No
No
NA
No
Yes
No
Yes
Yes
No
Yes
No
NA
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
No
NA
NA
No
No
NA
No
Yes
No
No
No
NA
No
No
NA
No
No
NA
No
No
No
No
Yes
No
Yes
No
NA
Yes
No
NA
No
No
NA
Yes
No
No
Test results
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
False
Correct
Correct
False
Correct
Correct
False
Correct
Correct
Correct
False
Correct
False
Correct
Correct
False
Correct
Correct
False
Correct
Correct
Correct
Correct
Correct
False
Correct
Correct
False
Correct
Correct
Correct
Correct
Correct
False
Correct
Correct
False
Correct
Correct
False
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
False
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
False
Correct
Correct
False
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
Correct
False