Member State report / Art8 / 2018 / D3 / Italy / Mediterranean: Ionian Sea & Central Mediterranean Sea
Report type | Member State report to Commission |
MSFD Article | Art. 8 Initial assessment (and Art. 17 updates) |
Report due | 2018-10-15 |
GES Descriptor | D3 Commercial fish and shellfish |
Member State | Italy |
Region/subregion | Mediterranean: Ionian Sea & Central Mediterranean Sea |
Reported by | ISPRA - Italian National Institute for Environmental Protection and Research |
Report date | 2020-10-01 |
Report access | MSFD_2018_ART8_GES_IT_2020-07-31.xml |
Ionian Sea and Central Mediterranean Sea (IT-ISCMS-0001)
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
|
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
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
|
Element |
Aristaeomorpha foliacea |
Aristaeomorpha foliacea |
Aristaeomorpha foliacea |
Aristaeomorpha foliacea |
Aristaeomorpha foliacea |
Aristaeomorpha foliacea |
Aristeus antennatus |
Aristeus antennatus |
Aristeus antennatus |
Engraulis encrasicolus |
Engraulis encrasicolus |
Engraulis encrasicolus |
Engraulis encrasicolus |
Engraulis encrasicolus |
Engraulis encrasicolus |
Merluccius merluccius |
Merluccius merluccius |
Merluccius merluccius |
Merluccius merluccius |
Merluccius merluccius |
Merluccius merluccius |
Mullus barbatus |
Mullus barbatus |
Mullus barbatus |
Mullus barbatus |
Mullus barbatus |
Mullus barbatus |
Mullus surmuletus |
Mullus surmuletus |
Mullus surmuletus |
Mullus surmuletus |
Mullus surmuletus |
Mullus surmuletus |
Nephrops norvegicus |
Nephrops norvegicus |
Nephrops norvegicus |
Pagellus erythrinus |
Pagellus erythrinus |
Pagellus erythrinus |
Parapenaeus longirostris |
Parapenaeus longirostris |
Parapenaeus longirostris |
Parapenaeus longirostris |
Parapenaeus longirostris |
Parapenaeus longirostris |
Sardina pilchardus |
Sardina pilchardus |
Sardina pilchardus |
Sardina pilchardus |
Sardina pilchardus |
Sardina pilchardus |
Element code |
158326 |
158326 |
158326 |
158326 |
158326 |
158326 |
107083 |
107083 |
107083 |
126426 |
126426 |
126426 |
126426 |
126426 |
126426 |
126484 |
126484 |
126484 |
126484 |
126484 |
126484 |
126985 |
126985 |
126985 |
126985 |
126985 |
126985 |
126986 |
126986 |
126986 |
126986 |
126986 |
126986 |
107254 |
107254 |
107254 |
127060 |
127060 |
127060 |
107109 |
107109 |
107109 |
107109 |
107109 |
107109 |
126421 |
126421 |
126421 |
126421 |
126421 |
126421 |
Element code source |
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Species (D1) http://www.marinespecies.org/
|
Element 2 |
Giant red shrimp (Aristaemorpha foliacea) in GSA 16 (Southern Sicily) |
Giant red shrimp (Aristaemorpha foliacea) in GSA 16 (Southern Sicily) |
Giant red shrimp (Aristaemorpha foliacea) in GSA 16 (Southern Sicily) |
Giant red shrimp (Aristaemorpha foliacea) in GSA 19 (Western Ionian Sea) |
Giant red shrimp (Aristaemorpha foliacea) in GSA 19 (Western Ionian Sea) |
Giant red shrimp (Aristaemorpha foliacea) in GSA 19 (Western Ionian Sea) |
Blue and red shrimp (Aristeus antennatus) in GSA 19 (Western Ionian Sea) |
Blue and red shrimp (Aristeus antennatus) in GSA 19 (Western Ionian Sea) |
Blue and red shrimp (Aristeus antennatus) in GSA 19 (Western Ionian Sea) |
Anchovy (Engraulis encrasicolus) in GSA 16 (Southern Sicily) |
Anchovy (Engraulis encrasicolus) in GSA 16 (Southern Sicily) |
Anchovy (Engraulis encrasicolus) in GSA 16 (Southern Sicily) |
Anchovy (Engraulis encrasicolus) in GSA 19 (Western Ionian Sea) |
Anchovy (Engraulis encrasicolus) in GSA 19 (Western Ionian Sea) |
Anchovy (Engraulis encrasicolus) in GSA 19 (Western Ionian Sea) |
European hake (Merluccius merluccius) in GSA 16 (Southern Sicily) |
European hake (Merluccius merluccius) in GSA 16 (Southern Sicily) |
European hake (Merluccius merluccius) in GSA 16 (Southern Sicily) |
European hake (Merluccius merluccius) in GSA 19 (Western Ionian Sea) |
European hake (Merluccius merluccius) in GSA 19 (Western Ionian Sea) |
European hake (Merluccius merluccius) in GSA 19 (Western Ionian Sea) |
Red mullet (Mullus barbatus) in GSA 16 (Southern Sicily) |
Red mullet (Mullus barbatus) in GSA 16 (Southern Sicily) |
Red mullet (Mullus barbatus) in GSA 16 (Southern Sicily) |
Red mullet (Mullus barbatus) in GSA 19 (Western Ionian Sea) |
Red mullet (Mullus barbatus) in GSA 19 (Western Ionian Sea) |
Red mullet (Mullus barbatus) in GSA 19 (Western Ionian Sea) |
Surmullet (Mullus surmuletus) in GSA 16 (Southern Sicily) |
Surmullet (Mullus surmuletus) in GSA 16 (Southern Sicily) |
Surmullet (Mullus surmuletus) in GSA 16 (Southern Sicily) |
Surmullet (Mullus surmuletus) in GSA 19 (Western Ionian Sea)
|
Surmullet (Mullus surmuletus) in GSA 19 (Western Ionian Sea)
|
Surmullet (Mullus surmuletus) in GSA 19 (Western Ionian Sea)
|
Norway lobster (Nephrops norvegicus) in GSA 16 (Southern Sicily) |
Norway lobster (Nephrops norvegicus) in GSA 16 (Southern Sicily) |
Norway lobster (Nephrops norvegicus) in GSA 16 (Southern Sicily) |
Common pandora (Pagellus erythrinus) in GSA 16 (Southern Sicily) |
Common pandora (Pagellus erythrinus) in GSA 16 (Southern Sicily) |
Common pandora (Pagellus erythrinus) in GSA 16 (Southern Sicily) |
Deep-water rose shrimp (Parapenaeus longirostris) in GSA 16 (Southern Sicily) |
Deep-water rose shrimp (Parapenaeus longirostris) in GSA 16 (Southern Sicily) |
Deep-water rose shrimp (Parapenaeus longirostris) in GSA 16 (Southern Sicily) |
Deep-water rose shrimp (Parapenaeus longirostris) in GSA 19 (Western Ionian Sea) |
Deep-water rose shrimp (Parapenaeus longirostris) in GSA 19 (Western Ionian Sea) |
Deep-water rose shrimp (Parapenaeus longirostris) in GSA 19 (Western Ionian Sea) |
Sardine (Sardina Pilchardus) in GSA 16 (Southern Sicily) |
Sardine (Sardina Pilchardus) in GSA 16 (Southern Sicily) |
Sardine (Sardina Pilchardus) in GSA 16 (Southern Sicily) |
Sardine (Sardina Pilchardus) in GSA 19 (Western Ionian Sea)
|
Sardine (Sardina Pilchardus) in GSA 19 (Western Ionian Sea) |
Sardine (Sardina Pilchardus) in GSA 19 (Western Ionian Sea)
|
Element 2 code |
ars.16
|
ars.16
|
ars.16
|
ars.19
|
ars.19
|
ars.19
|
ara.19
|
ara.19
|
ara.19
|
ane.16
|
ane.16
|
ane.16
|
ane.19
|
ane.19
|
ane.19
|
hke.16
|
hke.16
|
hke.16
|
hke.19
|
hke.19
|
hke.19
|
mut.16
|
mut.16
|
mut.16
|
mut.19
|
mut.19
|
mut.19
|
mur.16
|
mur.16
|
mur.16
|
mur.19
|
mur.19
|
mur.19
|
nep.16
|
nep.16
|
nep.16
|
pac.16
|
pac.16
|
pac.16
|
dps.16
|
dps.16
|
dps.16
|
dps.19
|
dps.19
|
dps.19
|
pil.16
|
pil.16
|
pil.16
|
pil.19
|
pil.19
|
pil.19
|
Element 2 code source |
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Species (D3) http://www.fao.org/fishery/collection/asfis/en
|
Element source |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
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
|
Parameter |
Mortality rate / Mortality rate from fishing (F)
|
BIOM-SSB
|
Mortality rate / Mortality rate from fishing (F)
|
BIOM-SSB
|
Mortality rate / Mortality rate from fishing (F)
|
BIOM-SSB
|
Mortality rate / Mortality rate from fishing (F)
|
BIOM-SSB
|
Mortality rate / Mortality rate from fishing (F)
|
BIOM-SSB
|
Mortality rate / Mortality rate from fishing (F)
|
BIOM-SSB
|
|||||||||||||||||||||||||||||||||||||||
Parameter other |
|||||||||||||||||||||||||||||||||||||||||||||||||||
Threshold value upper |
0.2 |
24.8 |
0.16 |
0.45 |
12.2 |
0.36 |
0.84 |
7.6 |
0.89 |
1028.0 |
|||||||||||||||||||||||||||||||||||||||||
Threshold value lower |
|||||||||||||||||||||||||||||||||||||||||||||||||||
Threshold qualitative |
|||||||||||||||||||||||||||||||||||||||||||||||||||
Threshold value source |
Common Fisheries Policy
|
General Fisheries Commission for the Mediterranean
|
Common Fisheries Policy
|
General Fisheries Commission for the Mediterranean
|
Common Fisheries Policy
|
General Fisheries Commission for the Mediterranean
|
Common Fisheries Policy
|
General Fisheries Commission for the Mediterranean
|
Common Fisheries Policy
|
General Fisheries Commission for the Mediterranean
|
Common Fisheries Policy
|
General Fisheries Commission for the Mediterranean
|
|||||||||||||||||||||||||||||||||||||||
Threshold value source other |
|||||||||||||||||||||||||||||||||||||||||||||||||||
Value achieved upper |
0.73 |
25.7 |
1.42 |
255.0 |
0.54 |
20.84 |
0.56 |
641.0 |
1.44 |
7.7 |
1.36 |
1644.0 |
|||||||||||||||||||||||||||||||||||||||
Value achieved lower |
|||||||||||||||||||||||||||||||||||||||||||||||||||
Value unit |
Other
|
tonne
|
Other
|
tonne
|
Other
|
tonne
|
Other
|
tonne
|
Other
|
tonne
|
Other
|
tonne
|
|||||||||||||||||||||||||||||||||||||||
Value unit other |
Natural logarithm of the ratio individuals over time |
Natural logarithm of the ratio individuals over time |
Natural logarithm of the ratio individuals over time |
Natural logarithm of the ratio individuals over time |
Natural logarithm of the ratio individuals over time |
Natural logarithm of the ratio individuals over time |
|||||||||||||||||||||||||||||||||||||||||||||
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 |
|||||||||||||||||||||||||||||||||||||||
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 |
|||||||||||||||||||||||||||||||||||||||
Trend |
Stable |
Stable |
Unknown |
Unknown |
Stable |
Improving |
Unknown |
Unknown |
Stable |
Stable |
Unknown |
Unknown |
|||||||||||||||||||||||||||||||||||||||
Parameter achieved |
No |
Yes |
No |
Not assessed |
No |
Yes |
No |
Not assessed |
No |
Yes |
No |
Yes |
|||||||||||||||||||||||||||||||||||||||
Description parameter |
|||||||||||||||||||||||||||||||||||||||||||||||||||
Related indicator |
|
|
|
|
|
|
|
|
|
|
|
|
|||||||||||||||||||||||||||||||||||||||
Criteria status |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not good |
Good |
Not assessed |
Not good |
Unknown |
Not assessed |
Not good |
Good |
Not assessed |
Not good |
Unknown |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not good |
Good |
Not assessed |
Not good |
Good |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Description criteria |
|||||||||||||||||||||||||||||||||||||||||||||||||||
Element status |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not good |
Not good |
Not good |
Not assessed |
Not assessed |
Not assessed |
Not good |
Not good |
Not good |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Description element |
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C1, D3C2 e D3C3 not assessed. Stock selected according to new GES definition. |
D3C1, D3C2 e D3C3 not assessed. Stock selected according to new GES definition. |
D3C1, D3C2 e D3C3 not assessed. Stock selected according to new GES definition. |
D3C1, D3C2 e D3C3 not assessed. Stock selected according to new GES definition. |
D3C1, D3C2 e D3C3 not assessed. Stock selected according to new GES definition. |
D3C1, D3C2 e D3C3 not assessed. Stock selected according to new GES definition. |
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C1, D3C2 e D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C1, D3C2 e D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C1, D3C2 e D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C1, D3C2 e D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C1, D3C2 e D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C1, D3C2 e D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C1, D3C2 e D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C1, D3C2 e D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C1, D3C2 e D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C3 not assessed. Stock selected being included as main stock or associated stock in the National Management Plan for demersal resources, i.e. "Decreto Ministeriale 30 gennaio 2018 - Adozione dei Piani di gestione nazionale relativi alle flotte di pesca per la cattura delle risorse demersali nell'ambito delle GSA 9, GSA 10, GSA 11, GSA 16, GSA 17 e 18, GSA 19".
|
D3C1, D3C2 e D3C3 not assessed. Stock selected according to new GES definition. |
D3C1, D3C2 e D3C3 not assessed. Stock selected according to new GES definition. |
D3C1, D3C2 e D3C3 not assessed. Stock selected according to new GES definition. |
D3C1, D3C2 e D3C3 not assessed. Stock selected according to new GES definition. |
D3C1, D3C2 e D3C3 not assessed. Stock selected according to new GES definition. |
D3C1, D3C2 e D3C3 not assessed. Stock selected according to new GES definition. |
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
|
Integration rule description parameter |
|||||||||||||||||||||||||||||||||||||||||||||||||||
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
|
Integration rule description criteria |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
To the purpose of this assessment we considered only D3C1 anbd D3C2 criteria, since methodologies for assessing D3C3 criteria are not yet consolidated at Mediterranean and suregional level. for GES assessement at stock level, the outcomes of assessments of criteria D3C1 and D3C2 were integrated: i) when both criteria provided a "good" status, the related stock was considered to be in "good" status; ii) when according to at least one criteria stock was assesed as being "no" good, the stock was reported to be in "no" good status; iii) when no criteria was available, or only one criteria was applied indicating the presence of a "good" status, status status was defined as being "unknown". GES was expressed as number (and percentage) of stocks that were in good status, no good status and unkonwn status. |
GES extent threshold |
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GES extent achieved |
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GES extent unit |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
Proportion of populations in good status |
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 expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
GES expected to be achieved later than 2020, no Article 14 exception reported |
Description overall status |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
As already known for the Mediterranean Sea, large share of the stocks assessed within each subregion is subject to unsustainable exploitation. In general, this condition is determined by excessive fishing mortality and, in some cases, inadequate spawning stock biomass. In addition, a high percentage of stocks (in particular in the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions) is not analytically assessed via stock assessment. In details, the Adriatic Sea is the subregion with the highest percentage of stocks within biological limits (14%); however, at the same time, it is the subregion presenting the highest percentage of stocks showing inadequate conditions (above 50% of stocks). In both the Western Mediterranean Sea and the Central Mediterranean and Ionian Sea subregions 76% of stocks are not assessed. However, while in the first case of the remaining stocks the 7% are in good conditions and 17% are not in good status, in the in the Central Mediterranean and Ionian Sea subregion all the remaining stocks (24%) are not within safe biological limits. Analyses to assess the status of each single stock in relation to F and SSB were applied according to the approach used by UNEP-MAP, 2018 (i.e. 2017 Mediterranean Quality Status Report, 539pp.), updated utilizing the lastest stock assessment from GFCM and STECF. |
Assessments period |
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