Member State report / Art8 / 2018 / D1-F / Portugal / NE Atlantic: Bay of Biscay & Iberian Coast
Report type | Member State report to Commission |
MSFD Article | Art. 8 Initial assessment (and Art. 17 updates) |
Report due | 2018-10-15 |
GES Descriptor | D1 Fish |
Member State | Portugal |
Region/subregion | NE Atlantic: Bay of Biscay & Iberian Coast |
Reported by | DGRM |
Report date | 2021-03-03 |
Report access | ART8_GES_PT_setembro2020.xml |
Portuguese Continent Subdivision (ABI-PT-SD-CONT)
GES component |
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
D1-F
|
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Feature |
Coastal fish
|
Coastal fish
|
Coastal fish
|
Coastal fish
|
Coastal fish
|
Coastal fish
|
Coastal fish
|
Coastal fish
|
Coastal fish
|
Coastal fish
|
Coastal fish
|
Coastal fish
|
Coastal fish
|
Coastal fish
|
Deep-sea fish
|
Deep-sea fish
|
Deep-sea fish
|
Deep-sea fish
|
Deep-sea fish
|
Deep-sea fish
|
Deep-sea fish
|
Deep-sea fish
|
Deep-sea fish
|
Deep-sea fish
|
Deep-sea fish
|
Deep-sea fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Pelagic shelf fish
|
Pelagic shelf fish
|
Pelagic shelf fish
|
Pelagic shelf fish
|
Pelagic shelf fish
|
Pelagic shelf fish
|
Pelagic shelf fish
|
Pelagic shelf fish
|
Pelagic shelf fish
|
Element |
Callionymus lyra |
Callionymus lyra |
Diplodus vulgaris |
Mullus surmuletus |
Pagellus acarne |
Pagellus erythrinus |
Pagellus erythrinus |
Pagellus erythrinus |
Serranus hepatus |
Serranus hepatus |
Serranus hepatus |
Spondyliosoma cantharus |
Spondyliosoma cantharus |
Spondyliosoma cantharus |
Chimaera monstrosa |
Chimaera monstrosa |
Deania spp. |
Deania spp. |
Etmopterus spinax |
Etmopterus spinax |
Galeus melastomus |
Malacocephalus laevis |
Malacocephalus laevis |
Nezumia sclerorhynchus |
Nezumia sclerorhynchus |
Phycis blennoides |
Argentina sphyraena |
Argentina sphyraena |
Argentina sphyraena |
Gadiculus argenteus |
Gadiculus argenteus |
Lepidorhombus boscii |
Lepidorhombus boscii |
Lepidorhombus boscii |
Lepidotrigla spp. |
Lepidotrigla spp. |
Leucoraja naevus |
Lophius budegassa |
Lophius budegassa |
Lophius budegassa |
Merluccius merluccius |
Merluccius merluccius |
Merluccius merluccius |
Microchirus variegatus |
Microchirus variegatus |
Micromesistius poutassou |
Micromesistius poutassou |
Micromesistius poutassou |
Raja clavata |
Scomber scombrus |
Scomber scombrus |
Scomber scombrus |
Scyliorhinus canicula |
Trachurus picturatus |
Trachurus trachurus |
Trachurus trachurus |
Trachurus trachurus |
Zeus faber |
Boops boops |
Capros aper |
Capros aper |
Capros aper |
Engraulis encrasicolus |
Sardina pilchardus |
Sardina pilchardus |
Sardina pilchardus |
Scomber colias |
Element code |
126792 |
126792 |
127054 |
126986 |
127057 |
127060 |
127060 |
127060 |
127042 |
127042 |
127042 |
127066 |
127066 |
127066 |
105824 |
105824 |
105771 |
105771 |
105913 |
105913 |
105812 |
272392 |
272392 |
126475 |
126475 |
126501 |
126716 |
126716 |
126716 |
126435 |
126435 |
127145 |
127145 |
127145 |
126179 |
126179 |
105876 |
126554 |
126554 |
126554 |
126484 |
126484 |
126484 |
274304 |
274304 |
126439 |
126439 |
126439 |
105883 |
127023 |
127023 |
127023 |
105814 |
126821 |
126822 |
126822 |
126822 |
127427 |
127047 |
127419 |
127419 |
127419 |
126426 |
126421 |
126421 |
126421 |
151174 |
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/
|
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 |
Four-spot megrim (Lepidorhombus boscii) in divisions 8.c and 9.a (southern Bay of Biscay and Atlantic Iberian waters East) |
Four-spot megrim (Lepidorhombus boscii) in divisions 8.c and 9.a (southern Bay of Biscay and Atlantic Iberian waters East) |
Four-spot megrim (Lepidorhombus boscii) in divisions 8.c and 9.a (southern Bay of Biscay and Atlantic Iberian waters East) |
Black-bellied anglerfish (Lophius budegassa) in divisions 8.c and 9.a (Cantabrian Sea, Atlantic Iberian waters) |
Black-bellied anglerfish (Lophius budegassa) in divisions 8.c and 9.a (Cantabrian Sea, Atlantic Iberian waters) |
Black-bellied anglerfish (Lophius budegassa) in divisions 8.c and 9.a (Cantabrian Sea, Atlantic Iberian waters) |
Hake (Merluccius merluccius) in divisions 8.c and 9.a, Southern stock (Cantabrian Sea and Atlantic Iberian waters) |
Hake (Merluccius merluccius) in divisions 8.c and 9.a, Southern stock (Cantabrian Sea and Atlantic Iberian waters) |
Hake (Merluccius merluccius) in divisions 8.c and 9.a, Southern stock (Cantabrian Sea and Atlantic Iberian waters) |
Blue whiting (Micromesistius poutassou) in subareas 1–9, 12, and 14 (Northeast Atlantic and adjacent waters) |
Blue whiting (Micromesistius poutassou) in subareas 1–9, 12, and 14 (Northeast Atlantic and adjacent waters) |
Blue whiting (Micromesistius poutassou) in subareas 1–9, 12, and 14 (Northeast Atlantic and adjacent waters) |
Mackerel (Scomber scombrus) in subareas 1–8 and 14, and in Division 9.a (the Northeast Atlantic and adjacent waters) |
Mackerel (Scomber scombrus) in subareas 1–8 and 14, and in Division 9.a (the Northeast Atlantic and adjacent waters) |
Mackerel (Scomber scombrus) in subareas 1–8 and 14, and in Division 9.a (the Northeast Atlantic and adjacent waters) |
Horse mackerel (Trachurus trachurus) in Division 9.a (Atlantic Iberian waters) |
Horse mackerel (Trachurus trachurus) in Division 9.a (Atlantic Iberian waters) |
Horse mackerel (Trachurus trachurus) in Division 9.a (Atlantic Iberian waters) |
Sardine (Sardina pilchardus) in divisions 8.c and 9.a (Cantabrian Sea and Atlantic Iberian waters) |
Sardine (Sardina pilchardus) in divisions 8.c and 9.a (Cantabrian Sea and Atlantic Iberian waters) |
Sardine (Sardina pilchardus) in divisions 8.c and 9.a (Cantabrian Sea and Atlantic Iberian waters) |
||||||||||||||||||||||||||||||||||||||||||||||
Element 2 code |
ldb.27.8c9a
|
ldb.27.8c9a
|
ldb.27.8c9a
|
ank.27.8c9a
|
ank.27.8c9a
|
ank.27.8c9a
|
hke.27.8c9a
|
hke.27.8c9a
|
hke.27.8c9a
|
whb.27.1-91214
|
whb.27.1-91214
|
whb.27.1-91214
|
mac.27.nea
|
mac.27.nea
|
mac.27.nea
|
hom.27.9a
|
hom.27.9a
|
hom.27.9a
|
pil.27.8c9a
|
pil.27.8c9a
|
pil.27.8c9a
|
||||||||||||||||||||||||||||||||||||||||||||||
Element 2 code source |
Species (D3) http://vocab.ices.dk/?ref=357
|
Species (D3) http://vocab.ices.dk/?ref=357
|
Species (D3) http://vocab.ices.dk/?ref=357
|
Species (D3) http://vocab.ices.dk/?ref=357
|
Species (D3) http://vocab.ices.dk/?ref=357
|
Species (D3) http://vocab.ices.dk/?ref=357
|
Species (D3) http://vocab.ices.dk/?ref=357
|
Species (D3) http://vocab.ices.dk/?ref=357
|
Species (D3) http://vocab.ices.dk/?ref=357
|
Species (D3) http://vocab.ices.dk/?ref=357
|
Species (D3) http://vocab.ices.dk/?ref=357
|
Species (D3) http://vocab.ices.dk/?ref=357
|
Species (D3) http://vocab.ices.dk/?ref=357
|
Species (D3) http://vocab.ices.dk/?ref=357
|
Species (D3) http://vocab.ices.dk/?ref=357
|
Species (D3) http://vocab.ices.dk/?ref=357
|
Species (D3) http://vocab.ices.dk/?ref=357
|
Species (D3) http://vocab.ices.dk/?ref=357
|
Species (D3) http://vocab.ices.dk/?ref=357
|
Species (D3) http://vocab.ices.dk/?ref=357
|
Species (D3) http://vocab.ices.dk/?ref=357
|
||||||||||||||||||||||||||||||||||||||||||||||
Element source |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
Criterion |
D1C1
|
D1C2
|
D1C1
|
D1C2
|
D1C3
|
D1C1
|
D1C2
|
D1C3
|
D1C1
|
D1C2
|
D1C3
|
D1C1
|
D1C2
|
D1C1
|
D1C2
|
D1C1
|
D1C2
|
D1C1
|
D1C2
|
D1C1
|
D1C2
|
D1C1
|
D1C2
|
D1C3
|
D1C1
|
D1C2
|
D1C1
|
D1C2
|
D1C3
|
D1C1
|
D1C2
|
D1C1
|
D1C2
|
D1C3
|
D1C1
|
D1C2
|
D1C3
|
D1C1
|
D1C2
|
D1C1
|
D1C2
|
D1C3
|
D1C1
|
D1C2
|
D1C3
|
D1C1
|
D1C2
|
D1C3
|
D1C1
|
D1C2
|
D1C3
|
D1C1
|
D1C2
|
D1C3
|
|||||||||||||
Parameter |
Biomass
|
Biomass
|
Other
|
Biomass
|
Other
|
Biomass
|
Other
|
Biomass
|
Biomass
|
Biomass
|
Biomass
|
Biomass
|
Biomass
|
Other
|
Biomass
|
Other
|
Other
|
Biomass
|
Other
|
Other
|
Other
|
Other
|
Biomass
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Biomass
|
Other
|
Other
|
Other
|
||||||||||||||||||||||||||||||||||
Parameter other |
L95
|
L95
|
L95
|
L95
|
Biomass of spawning Stock (SSB)
|
Size distribution
|
MSY Btrigger proxy
|
Size distribution
|
Biomass of spawning Stock (SSB)
|
Size distribution
|
Biomass of spawning Stock (SSB)
|
Size distribution
|
Biomass of spawning Stock (SSB)
|
Size distribution
|
Biomass of spawning Stock (SSB)
|
Size distribution
|
L95
|
Biomass of spawning Stock (SSB)
|
Size distribution
|
||||||||||||||||||||||||||||||||||||||||||||||||
Threshold value upper |
4600.0 |
0.5 |
11100.0 |
2250000.0 |
2570000.0 |
181000.0 |
446331.0 |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Threshold value lower |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Threshold qualitative |
Combination of break-point analysis with trend over the last 5 years (Probst and Steelzenmuller, 2015 method)
|
Combination of break-point analysis with trend over the last 5 years (Probst and Steelzenmuller, 2015 method)
|
Combination of break-point analysis with trend over the last 5 years (Probst and Steelzenmuller, 2015 method)
|
Combination of break-point analysis with trend over the last 5 years (Probst and Steelzenmuller, 2015 method)
|
Combination of break-point analysis with trend over the last 5 years (Probst and Steelzenmuller, 2015 method)
|
Combination of break-point analysis with trend over the last 5 years (Probst and Steelzenmuller, 2015 method)
|
Combination of break-point analysis with trend over the last 5 years (Probst and Steelzenmuller, 2015 method)
|
Combination of break-point analysis with trend over the last 5 years (Probst and Steelzenmuller, 2015 method)
|
Combination of break-point analysis with trend over the last 5 years (Probst and Steelzenmuller, 2015 method)
|
Combination of break-point analysis with trend over the last 5 years (Probst and Steelzenmuller, 2015 method)
|
Combination of break-point analysis with trend over the last 5 years (Probst and Steelzenmuller, 2015 method)
|
Combination of break-point analysis with trend over the last 5 years (Probst and Steelzenmuller, 2015 method)
|
Combination of break-point analysis with trend over the last 5 years (Probst and Steelzenmuller, 2015 method)
|
Combination of break-point analysis with trend over the last 5 years (Probst and Steelzenmuller, 2015 method)
|
|||||||||||||||||||||||||||||||||||||||||||||||||||||
Threshold value source |
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
||||||||||||||||||||||||||||||||||||||||||||||
Threshold value source other |
Probst, W. N., Stelzenmuller, V. (2015). A benchmarking and assessment framework to operationalise ecological indicators based on time series analysis, Ecological Indicators, 55: 94-106. |
Probst, W. N., Stelzenmuller, V. (2015). A benchmarking and assessment framework to operationalise ecological indicators based on time series analysis, Ecological Indicators, 55: 94-106. |
Probst, W. N., Stelzenmuller, V. (2015). A benchmarking and assessment framework to operationalise ecological indicators based on time series analysis, Ecological Indicators, 55: 94-106. |
Probst, W. N., Stelzenmuller, V. (2015). A benchmarking and assessment framework to operationalise ecological indicators based on time series analysis, Ecological Indicators, 55: 94-106. |
Probst, W. N., Stelzenmuller, V. (2015). A benchmarking and assessment framework to operationalise ecological indicators based on time series analysis, Ecological Indicators, 55: 94-106. |
Probst, W. N., Stelzenmuller, V. (2015). A benchmarking and assessment framework to operationalise ecological indicators based on time series analysis, Ecological Indicators, 55: 94-106. |
Probst, W. N., Stelzenmuller, V. (2015). A benchmarking and assessment framework to operationalise ecological indicators based on time series analysis, Ecological Indicators, 55: 94-106. |
Probst, W. N., Stelzenmuller, V. (2015). A benchmarking and assessment framework to operationalise ecological indicators based on time series analysis, Ecological Indicators, 55: 94-106. |
Probst, W. N., Stelzenmuller, V. (2015). A benchmarking and assessment framework to operationalise ecological indicators based on time series analysis, Ecological Indicators, 55: 94-106. |
Probst, W. N., Stelzenmuller, V. (2015). A benchmarking and assessment framework to operationalise ecological indicators based on time series analysis, Ecological Indicators, 55: 94-106. |
Probst, W. N., Stelzenmuller, V. (2015). A benchmarking and assessment framework to operationalise ecological indicators based on time series analysis, Ecological Indicators, 55: 94-106. |
International Council for the Exploration of the Sea (ICES) |
Probst, W. N., Stelzenmuller, V. (2015). A benchmarking and assessment framework to operationalise ecological indicators based on time series analysis, Ecological Indicators, 55: 94-106. |
International Council for the Exploration of the Sea (ICES) |
International Council for the Exploration of the Sea (ICES) |
Probst, W. N., Stelzenmuller, V. (2015). A benchmarking and assessment framework to operationalise ecological indicators based on time series analysis, Ecological Indicators, 55: 94-106. |
International Council for the Exploration of the Sea (ICES) |
International Council for the Exploration of the Sea (ICES) |
International Council for the Exploration of the Sea (ICES) |
Probst, W. N., Stelzenmuller, V. (2015). A benchmarking and assessment framework to operationalise ecological indicators based on time series analysis, Ecological Indicators, 55: 94-106. |
International Council for the Exploration of the Sea (ICES) |
||||||||||||||||||||||||||||||||||||||||||||||
Value achieved upper |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Value achieved lower |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Value unit |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Value unit other |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Proportion threshold value |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Proportion value achieved |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Proportion threshold value unit |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Trend |
Improving |
Improving |
Stable |
Deteriorating |
Stable |
Deteriorating |
Deteriorating |
Improving |
Stable |
Improving |
Deteriorating |
Improving |
Improving |
Stable |
Stable |
Improving |
Unknown |
Improving |
Stable |
Unknown |
Improving |
Unknown |
Improving |
Improving |
Unknown |
Deteriorating |
Unknown |
Stable |
Unknown |
Improving |
Improving |
Deteriorating |
Unknown |
||||||||||||||||||||||||||||||||||
Parameter achieved |
Yes |
Yes |
Not assessed |
Yes |
Not assessed |
Yes |
Not assessed |
Yes |
Yes |
Yes |
Yes |
Yes |
Yes |
Not assessed |
Yes |
Yes |
Unknown |
Yes |
Yes |
Unknown |
Yes |
Unknown |
Yes |
Yes |
Unknown |
Yes |
Unknown |
Yes |
Unknown |
Yes |
Not assessed |
No |
Unknown |
||||||||||||||||||||||||||||||||||
Description parameter |
GES assessment was based on the method proposed by Problem and Steelzenmuller (2015) ?me-series assessment and benchmarking of ecological indicators?. Although the average of the series in the assessment period is below the estimated average for the reference period (0.05 and 0.11, respectively), the trend analysis indicates that the trend 2013-2017 is positive. For this reason the biomass of the species was found to be at favourable levels.
|
GES assessment was based on the method proposed by Problem and Steelzenmuller (2015) ?me-series assessment and benchmarking of ecological indicators?. The average of the series in the assessment period was higher than the estimated average for the reference period (8.21 and 1.19, respectively), the trend analysis indicates that the trend 2013-2017 is positive. For this reason the biomass of the species was found to be at favourable levels.
|
The 95th percentile of the annual distribution by length (L95) (ICES, 2017) has been estimated. It will not contribute to the determination of GES because of the need for further studies to verify the appropriateness of the method to meet the criterion, and to define reference points and the respective assessment thresholds (ICES, 2017).
ICES (2017). EU request to provide guidance on operational methods for the evaluation of the MSFD Criteria teriion D3C3 (second step 2017). In Report of the ICES Special Request Advice, 2017. ICES Advice 2017, sr.2017.07.
|
GES assessment was based on the method proposed by Problem and Steelzenmuller (2015) ?me-series assessment and benchmarking of ecological indicators?. The average of the series in the assessment period was higher than the estimated average for the reference period (0.63 and 0.28, respectively). For this reason, and although the trend analysis indicates that the trend 2013-2017 is decreasing, the biomass of the species was considered to be at favourable levels.
|
The 95th percentile of the annual distribution by length (L95) (ICES, 2017) has been estimated. It will not contribute to the determination of GES because of the need for further studies to verify the appropriateness of the method to meet the criterion, and to define reference points and the respective assessment thresholds (ICES, 2017).
ICES (2017). EU request to provide guidance on operational methods for the evaluation of the MSFD Criteria teriion D3C3 (second step 2017). In Report of the ICES Special Request Advice, 2017. ICES Advice 2017, sr.2017.07.
|
GES assessment was based on the method proposed by Problem and Steelzenmuller (2015) ?me-series assessment and benchmarking of ecological indicators?. The average of the series in the assessment period was well above the estimated average for the reference period (4.24 and 0.67, respectively). For this reason, and while the trend analysis indicates that the trend 2013-2017 is decreasing, the biomass of the species was considered to be at favourable levels.
|
The 95th percentile of the annual distribution by length (L95) (ICES, 2017) has been estimated. It will not contribute to the determination of GES because of the need for further studies to verify the appropriateness of the method to meet the criterion, and to define reference points and the respective assessment thresholds (ICES, 2017).
ICES (2017). EU request to provide guidance on operational methods for the evaluation of the MSFD Criteria teriion D3C3 (second step 2017). In Report of the ICES Special Request Advice, 2017. ICES Advice 2017, sr.2017.07.
|
GES assessment was based on the method proposed by Problem and Steelzenmuller (2015) ?me-series assessment and benchmarking of ecological indicators?. The average of the series in the assessment period was higher than the estimated average for the reference period (4.69 and 1.37, respectively) and the trend analysis indicates that the trend 2013-2017 is positive. For this reason the biomass of the species was found to be at favourable levels.
|
GES assessment was based on the method proposed by Problem and Steelzenmuller (2015) ?me-series assessment and benchmarking of ecological indicators?. Although the average of the series in the assessment period is below the estimated average for the reference period (0.94 and 1.16, respectively), this difference is not statistically significant. On the other hand, the trend analysis indicates that the trend 2013-2017 is positive. For this reason the biomass of the species was found to be at favourable levels.
|
GES assessment was based on the method proposed by Problem and Steelzenmuller (2015) ?me-series assessment and benchmarking of ecological indicators?. The average of the series in the assessment period was higher than the estimated average for the reference period (0.75 and 0.57, respectively). For this reason, and while the trend analysis indicates that the trend 2013-2017 is decreasing, the biomass of the species was considered to be at favourable levels.
|
GES assessment was based on the method proposed by Problem and Steelzenmuller (2015) ?me-series assessment and benchmarking of ecological indicators?. Although the average of the series in the assessment period is below the estimated average for the reference period (2.93 and 3.28, respectively), this difference is not statistically significant. On the other hand, the trend analysis indicates that the trend 2013-2017 is positive. For this reason the biomass of the species was found to be at favourable levels.
|
GES assessment was based on the method proposed by Problem and Steelzenmuller (2015) ?me-series assessment and benchmarking of ecological indicators?. Although the average of the series in the assessment period is below the estimated average for the reference period (0.10 and 0.25, respectively), the trend analysis indicates that the trend 2013-2017 is positive. For this reason the biomass of the species was found to be at favourable levels.
|
The 95th percentile of the annual distribution by length (L95) (ICES, 2017) has been estimated. It will not contribute to the determination of GES because of the need for further studies to verify the appropriateness of the method to meet the criterion, and to define reference points and the respective assessment thresholds (ICES, 2017).
ICES (2017). EU request to provide guidance on operational methods for the evaluation of the MSFD Criteria teriion D3C3 (second step 2017). In Report of the ICES Special Request Advice, 2017. ICES Advice 2017, sr.2017.07.
|
GES assessment was based on the method proposed by Problem and Steelzenmuller (2015) ?me-series assessment and benchmarking of ecological indicators?. The average of the series in the assessment period was higher than the estimated average for the reference period (1.30 and 0.17, respectively) and the trend analysis indicates that the trend 2013-2017 is positive. For this reason the biomass of the species was found to be at favourable levels.
|
GES assessment was based on the method proposed by Problem and Steelzenmuller (2015) ?me-series assessment and benchmarking of ecological indicators?. Although the average of the series in the assessment period is below the estimated average for the reference period (0.13 and 0.17, respectively), this difference is not statistically significant. On the other hand, the trend analysis indicates that the trend 2013-2017 is positive. For this reason the biomass of the species was found to be at favourable levels.
|
GES assessment was based on the method proposed by Problem and Steelzenmuller (2015) ?me-series assessment and benchmarking of ecological indicators?. The average of the series in the assessment period was higher than the estimated average for the reference period (15.90 and 14.27, respectively) and the trend analysis indicates that the trend 2013-2017 is positive. For this reason the biomass of the species was found to be at favourable levels.
|
The 95th percentile of the annual distribution by length (L95) (ICES, 2017) has been estimated. It will not contribute to the determination of GES because of the need for further studies to verify the appropriateness of the method to meet the criterion, and to define reference points and the respective assessment thresholds (ICES, 2017).
ICES (2017). EU request to provide guidance on operational methods for the evaluation of the MSFD Criteria teriion D3C3 (second step 2017). In Report of the ICES Special Request Advice, 2017. ICES Advice 2017, sr.2017.07.
|
||||||||||||||||||||||||||||||||||||||||||||||||||
Related indicator |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Criteria status |
Not assessed |
Good |
Not assessed |
Good |
Not assessed |
Not assessed |
Good |
Not assessed |
Not assessed |
Good |
Not assessed |
Not assessed |
Good |
Not assessed |
Good |
Not assessed |
Good |
Not assessed |
Good |
Not assessed |
Good |
Not assessed |
Good |
Not assessed |
Not assessed |
Good |
Not assessed |
Good |
Unknown |
Not assessed |
Good |
Not assessed |
Good |
Unknown |
Not assessed |
Good |
Unknown |
Not assessed |
Good |
Not assessed |
Good |
Unknown |
Not assessed |
Good |
Unknown |
Not assessed |
Good |
Unknown |
Not assessed |
Good |
Not assessed |
Not assessed |
Not good |
Unknown |
|||||||||||||
Description criteria |
No assessment of status of criterion D1C1 was carried out. There is little information dependent on fisheries as these non-commercial species are generally rejected by commercial fleets. In view of the above, and given the inaccuracies in the catch estimates, it was concluded that neither the proposed data nor the proposed methods allow to characterise and assess the test with confidence. In addition, thresholds for the classification of GES are not yet defined.
|
No assessment of status of criterion D1C1 was carried out. There is little information dependent on fisheries as these non-commercial species are generally rejected by commercial fleets. In view of the above, and given the inaccuracies in the catch estimates, it was concluded that neither the proposed data nor the proposed methods allow to characterise and assess the test with confidence. In addition, thresholds for the classification of GES are not yet defined.
|
No assessment of status of criterion D1C1 was carried out. There is little information dependent on fisheries as these non-commercial species are generally rejected by commercial fleets. In view of the above, and given the inaccuracies in the catch estimates, it was concluded that neither the proposed data nor the proposed methods allow to characterise and assess the test with confidence. In addition, thresholds for the classification of GES are not yet defined.
|
No assessment of status of criterion D1C1 was carried out. There is little information dependent on fisheries as these non-commercial species are generally rejected by commercial fleets. In view of the above, and given the inaccuracies in the catch estimates, it was concluded that neither the proposed data nor the proposed methods allow to characterise and assess the test with confidence. In addition, thresholds for the classification of GES are not yet defined.
|
No assessment of status of criterion D1C1 was carried out. There is little information dependent on fisheries as these non-commercial species are generally rejected by commercial fleets. In view of the above, and given the inaccuracies in the catch estimates, it was concluded that neither the proposed data nor the proposed methods allow to characterise and assess the test with confidence. In addition, thresholds for the classification of GES are not yet defined.
|
No assessment of status of criterion D1C1 was carried out. There is little information dependent on fisheries as these non-commercial species are generally rejected by commercial fleets. In view of the above, and given the inaccuracies in the catch estimates, it was concluded that neither the proposed data nor the proposed methods allow to characterise and assess the test with confidence. In addition, thresholds for the classification of GES are not yet defined.
|
No assessment of status of criterion D1C1 was carried out. There is little information dependent on fisheries as these non-commercial species are generally rejected by commercial fleets. In view of the above, and given the inaccuracies in the catch estimates, it was concluded that neither the proposed data nor the proposed methods allow to characterise and assess the test with confidence. In addition, thresholds for the classification of GES are not yet defined.
|
No assessment of status of criterion D1C1 was carried out. There is little information dependent on fisheries as these non-commercial species are generally rejected by commercial fleets. In view of the above, and given the inaccuracies in the catch estimates, it was concluded that neither the proposed data nor the proposed methods allow to characterise and assess the test with confidence. In addition, thresholds for the classification of GES are not yet defined.
|
No assessment of status of criterion D1C1 was carried out. There is little information dependent on fisheries as these non-commercial species are generally rejected by commercial fleets. In view of the above, and given the inaccuracies in the catch estimates, it was concluded that neither the proposed data nor the proposed methods allow to characterise and assess the test with confidence. In addition, thresholds for the classification of GES are not yet defined.
|
No assessment of status of criterion D1C1 was carried out. There is little information dependent on fisheries as these non-commercial species are generally rejected by commercial fleets. In view of the above, and given the inaccuracies in the catch estimates, it was concluded that neither the proposed data nor the proposed methods allow to characterise and assess the test with confidence. In addition, thresholds for the classification of GES are not yet defined.
|
No assessment of status of criterion D1C1 was carried out. There is little information dependent on fisheries as these non-commercial species are generally rejected by commercial fleets. In view of the above, and given the inaccuracies in the catch estimates, it was concluded that neither the proposed data nor the proposed methods allow to characterise and assess the test with confidence. In addition, thresholds for the classification of GES are not yet defined.
|
Not applicable to this species (species of commercial interest). ?Fishing mortality rate (F)?, as measured in ?descriptor 3? (D3C1).
|
Assessment under Descriptor 3 (D3C2).
|
Assessment under Descriptor 3 (D3C3):
The ICES has recommended the use of Age Based Indicators (IBI) as these are derived from assessments based on a more robust analysis of the population structure. Currently, the number of stocks for which the assessment of this indicator is available is however very limited.
The ICES has analysed the proposed methods for criterion D3C3 on stocks with quantitative evaluation and concluded that they were not yet operational for the assessment of good environmental status (ICES, 2017a
|
No assessment of status of criterion D1C1 was carried out. There is little information dependent on fisheries as these non-commercial species are generally rejected by commercial fleets. In view of the above, and given the inaccuracies in the catch estimates, it was concluded that neither the proposed data nor the proposed methods allow to characterise and assess the test with confidence. In addition, thresholds for the classification of GES are not yet defined.
|
Not applicable to this species (species of commercial interest). ?Fishing mortality rate (F)?, as measured in ?descriptor 3? (D3C1).
|
Assessment under Descriptor 3 (D3C2).
|
Assessment under Descriptor 3 (D3C3).
The ICES has recommended the use of Age Based Indicators (IBI) as these are derived from assessments based on a more robust analysis of the population structure. Currently, the number of stocks for which the assessment of this indicator is available is however very limited.
The ICES has analysed the proposed methods for criterion D3C3 on stocks with quantitative evaluation and concluded that they were not yet operational for the assessment of good environmental status (ICES, 2017a
|
Not applicable to this species (species of commercial interest). ?Fishing mortality rate (F)?, as measured in ?descriptor 3? (D3C1).
|
Assessment under Descriptor 3 (D3C2).
|
Assessment under Descriptor 3 (D3C3).
The ICES has recommended the use of Age Based Indicators (IBI) as these are derived from assessments based on a more robust analysis of the population structure. Currently, the number of stocks for which the assessment of this indicator is available is however very limited.
The ICES has analysed the proposed methods for criterion D3C3 on stocks with quantitative evaluation and concluded that they were not yet operational for the assessment of good environmental status (ICES, 2017a
|
No assessment of status of criterion D1C1 was carried out. There is little information dependent on fisheries as these non-commercial species are generally rejected by commercial fleets. In view of the above, and given the inaccuracies in the catch estimates, it was concluded that neither the proposed data nor the proposed methods allow to characterise and assess the test with confidence. In addition, thresholds for the classification of GES are not yet defined.
|
Not applicable to this species (species of commercial interest). ?Fishing mortality rate (F)?, as measured in ?descriptor 3? (D3C1).
|
Assessment under Descriptor 3 (D3C2).
|
Assessment under Descriptor 3 (D3C3).
The ICES has recommended the use of Age Based Indicators (IBI) as these are derived from assessments based on a more robust analysis of the population structure. Currently, the number of stocks for which the assessment of this indicator is available is however very limited.
The ICES has analysed the proposed methods for criterion D3C3 on stocks with quantitative evaluation and concluded that they were not yet operational for the assessment of good environmental status (ICES, 2017a
|
Not applicable to this species (species of commercial interest). ?Fishing mortality rate (F)?, as measured in ?descriptor 3? (D3C1).
|
Assessment under Descriptor 3 (D3C2).
|
Assessment under Descriptor 3 (D3C3).
The ICES has recommended the use of Age Based Indicators (IBI) as these are derived from assessments based on a more robust analysis of the population structure. Currently, the number of stocks for which the assessment of this indicator is available is however very limited.
The ICES has analysed the proposed methods for criterion D3C3 on stocks with quantitative evaluation and concluded that they were not yet operational for the assessment of good environmental status (ICES, 2017a
|
Not applicable to this species (species of commercial interest). ?Fishing mortality rate (F)?, as measured in ?descriptor 3? (D3C1).
|
Assessment under Descriptor 3 (D3C2).
|
Assessment under Descriptor 3 (D3C3).
The ICES has recommended the use of Age Based Indicators (IBI) as these are derived from assessments based on a more robust analysis of the population structure. Currently, the number of stocks for which the assessment of this indicator is available is however very limited.
The ICES has analysed the proposed methods for criterion D3C3 on stocks with quantitative evaluation and concluded that they were not yet operational for the assessment of good environmental status (ICES, 2017a
|
No assessment of status of criterion D1C1 was carried out. There is little information dependent on fisheries as these non-commercial species are generally rejected by commercial fleets. In view of the above, and given the inaccuracies in the catch estimates, it was concluded that neither the proposed data nor the proposed methods allow to characterise and assess the test with confidence. In addition, thresholds for the classification of GES are not yet defined.
|
Not applicable to this species (species of commercial interest). ?Fishing mortality rate (F)?, as measured in ?descriptor 3? (D3C1).
|
Assessment under Descriptor 3 (D3C2).
|
Assessment under Descriptor 3 (D3C3).
The ICES has recommended the use of Age Based Indicators (IBI) as these are derived from assessments based on a more robust analysis of the population structure. Currently, the number of stocks for which the assessment of this indicator is available is however very limited.
The ICES has analysed the proposed methods for criterion D3C3 on stocks with quantitative evaluation and concluded that they were not yet operational for the assessment of good environmental status (ICES, 2017a
|
||||||||||||||||||||||||||||||||
Element status |
Good |
Good |
Not assessed |
Not assessed |
Not assessed |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Not assessed |
Good |
Good |
Good |
Good |
Not assessed |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Not assessed |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Not assessed |
Good |
Good |
Good |
Not assessed |
Not assessed |
Good |
Good |
Good |
Not assessed |
Not assessed |
Good |
Good |
Good |
Not assessed |
Not good |
Not good |
Not good |
Not assessed |
Description element |
Assessment of the status of the species was based on the result of D1C2.
|
Assessment of the status of the species was based on the result of D1C2.
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
Assessment of the status of the species was based on the result of D1C2.
The information reported relates to the south-western and south areas of the waters of mainland Portugal (ABI_PT_AAG_CONAG_CONT_AAG_CONTACS), where the species is preferably distributed. However, the assessments of the status of the criteria and of the element have been included in the results for the whole of ABI_PT_AA_AGCON_AG_CONTAC_ACON_AG_CONTAC_AG_CONT_AG_CONT_CONT_C, since it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848.
|
Assessment of the status of the species was based on the result of D1C2.
The information reported relates to the south-western and south areas of the waters of mainland Portugal (ABI_PT_AAG_CONAG_CONT_AAG_CONTACS), where the species is preferably distributed. However, the assessments of the status of the criteria and of the element have been included in the results for the whole of ABI_PT_AA_AGCON_AG_CONTAC_ACON_AG_CONTAC_AG_CONT_AG_CONT_CONT_C, since it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848.
|
Assessment of the status of the species was based on the result of D1C2.
The information reported relates to the south-western and south areas of the waters of mainland Portugal (ABI_PT_AAG_CONAG_CONT_AAG_CONTACS), where the species is preferably distributed. However, the assessments of the status of the criteria and of the element have been included in the results for the whole of ABI_PT_AA_AGCON_AG_CONTAC_ACON_AG_CONTAC_AG_CONT_AG_CONT_CONT_C, since it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848.
|
Assessment of the status of the species was based on the result of D1C2.
The information reported relates to the south-western and south areas of the waters of mainland Portugal (ABI_PT_AAG_CONAG_CONT_AAG_CONTACS), where the species is preferably distributed. However, the assessments of the status of the criteria and of the element have been included in the results for the whole of ABI_PT_AA_AGCON_AG_CONTAC_ACON_AG_CONTAC_AG_CONT_AG_CONT_CONT_C, since it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848.
|
Assessment of the status of the species was based on the result of D1C2.
The information reported relates to the south-western and south areas of the waters of mainland Portugal (ABI_PT_AAG_CONAG_CONT_AAG_CONTACS), where the species is preferably distributed. However, the assessments of the status of the criteria and of the element have been included in the results for the whole of ABI_PT_AA_AGCON_AG_CONTAC_ACON_AG_CONTAC_AG_CONT_AG_CONT_CONT_C, since it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848.
|
Assessment of the status of the species was based on the result of D1C2.
The information reported relates to the south-western and south areas of the waters of mainland Portugal (ABI_PT_AAG_CONAG_CONT_AAG_CONTACS), where the species is preferably distributed. However, the assessments of the status of the criteria and of the element have been included in the results for the whole of ABI_PT_AA_AGCON_AG_CONTAC_ACON_AG_CONTAC_AG_CONT_AG_CONT_CONT_C, since it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848.
|
Assessment of the status of the species was based on the result of D1C2.
The information reported relates to the south-western and south areas of the waters of mainland Portugal (ABI_PT_AAG_CONAG_CONT_AAG_CONTACS), where the species is preferably distributed. However, the assessments of the status of the criteria and of the element have been included in the results for the whole of ABI_PT_AA_AGCON_AG_CONTAC_ACON_AG_CONTAC_AG_CONT_AG_CONT_CONT_C, since it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848.
|
Assessment of the status of the species was based on the result of D1C2.
The information reported relates to the south-western and south areas of the waters of mainland Portugal (ABI_PT_AAG_CONAG_CONT_AAG_CONTACS), where the species is preferably distributed. However, the assessments of the status of the criteria and of the element have been included in the results for the whole of ABI_PT_AA_AGCON_AG_CONTAC_ACON_AG_CONTAC_AG_CONT_AG_CONT_CONT_C, since it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848.
|
Assessment of the status of the species was based on the result of D1C2.
The information reported relates to the south-western and south areas of the waters of mainland Portugal (ABI_PT_AAG_CONAG_CONT_AAG_CONTACS), where the species is preferably distributed. However, the assessments of the status of the criteria and of the element have been included in the results for the whole of ABI_PT_AA_AGCON_AG_CONTAC_ACON_AG_CONTAC_AG_CONT_AG_CONT_CONT_C, since it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848.
|
Assessment of the status of the species was based on the result of D1C2.
The reported information refers to the south-western and southern mainland of mainland Portugal (ABI_PT_AA_CONTAC_AG_CONTAC-AAG_CONTACT), since the information deemed most suitable for assessing its biomass is collected in the IPMA crustacean campaign, which takes place in these areas only. However, the species has a wider distribution, so it is expected that the information submitted and its assessments reflect the trend of populations on our coast. The assessments of the status of the criteria and of the element have thus been included in the results for the whole of ABI_PT_AA_AGCON_AG_CONTAC_ACON_AG_CONT_AG_CONT_AG_CONT_CONT_C, since it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848.
|
Assessment of the status of the species was based on the result of D1C2.
The reported information refers to the south-western and southern mainland of mainland Portugal (ABI_PT_AA_CONTAC_AG_CONTAC-AAG_CONTACT), since the information deemed most suitable for assessing its biomass is collected in the IPMA crustacean campaign, which takes place in these areas only. However, the species has a wider distribution, so it is expected that the information submitted and its assessments reflect the trend of populations on our coast. The assessments of the status of the criteria and of the element have thus been included in the results for the whole of ABI_PT_AA_AGCON_AG_CONTAC_ACON_AG_CONT_AG_CONT_AG_CONT_CONT_C, since it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848.
|
Radcliffe, 1912) but may include some persons Deania calcea (Lowe, 1839).
The reported information refers to the south-western and southern mainland of mainland Portugal (ABI_PT_AA_CONTAC_AG_CONTAC-AAG_CONTACT), since the information deemed most suitable for assessing its biomass is collected in the IPMA crustacean campaign, which takes place in these areas only. However, the species has a wider distribution, so it is expected that the information submitted and its assessments reflect the trend of populations on our coast. The assessments of the status of the criteria and of the element have thus been included in the results for the whole of ABI_PT_AA_AGCON_AG_CONTAC_ACON_AG_CONT_AG_CONT_AG_CONT_CONT_C, since it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848.
|
Radcliffe, 1912) but may include some persons Deania calcea (Lowe, 1839).
The reported information refers to the south-western and southern mainland of mainland Portugal (ABI_PT_AA_CONTAC_AG_CONTAC-AAG_CONTACT), since the information deemed most suitable for assessing its biomass is collected in the IPMA crustacean campaign, which takes place in these areas only. However, the species has a wider distribution, so it is expected that the information submitted and its assessments reflect the trend of populations on our coast. The assessments of the status of the criteria and of the element have thus been included in the results for the whole of ABI_PT_AA_AGCON_AG_CONTAC_ACON_AG_CONT_AG_CONT_AG_CONT_CONT_C, since it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848.
|
Assessment of the status of the species was based on the result of D1C2.
The reported information refers to the south-western and southern mainland of mainland Portugal (ABI_PT_AA_CONTAC_AG_CONTAC-AAG_CONTACT), since the information deemed most suitable for assessing its biomass is collected in the IPMA crustacean campaign, which takes place in these areas only. However, the species has a wider distribution, so it is expected that the information submitted and its assessments reflect the trend of populations on our coast. The assessments of the status of the criteria and of the element have thus been included in the results for the whole of ABI_PT_AA_AGCON_AG_CONTAC_ACON_AG_CONT_AG_CONT_AG_CONT_CONT_C, since it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848.
|
Assessment of the status of the species was based on the result of D1C2.
The reported information refers to the south-western and southern mainland of mainland Portugal (ABI_PT_AA_CONTAC_AG_CONTAC-AAG_CONTACT), since the information deemed most suitable for assessing its biomass is collected in the IPMA crustacean campaign, which takes place in these areas only. However, the species has a wider distribution, so it is expected that the information submitted and its assessments reflect the trend of populations on our coast. The assessments of the status of the criteria and of the element have thus been included in the results for the whole of ABI_PT_AA_AGCON_AG_CONTAC_ACON_AG_CONT_AG_CONT_AG_CONT_CONT_C, since it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848.
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
Assessment of the status of the species was based on the result of D1C2.
The reported information refers to the south-western and southern mainland of mainland Portugal (ABI_PT_AA_CONTAC_AG_CONTAC-AAG_CONTACT), since the information deemed most suitable for assessing its biomass is collected in the IPMA crustacean campaign, which takes place in these areas only. However, the species has a wider distribution, so it is expected that the information submitted and its assessments reflect the trend of populations on our coast. The assessments of the status of the criteria and of the element have thus been included in the results for the whole of ABI_PT_AA_AGCON_AG_CONTAC_ACON_AG_CONT_AG_CONT_AG_CONT_CONT_C, since it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848.
|
Assessment of the status of the species was based on the result of D1C2.
The reported information refers to the south-western and southern mainland of mainland Portugal (ABI_PT_AA_CONTAC_AG_CONTAC-AAG_CONTACT), since the information deemed most suitable for assessing its biomass is collected in the IPMA crustacean campaign, which takes place in these areas only. However, the species has a wider distribution, so it is expected that the information submitted and its assessments reflect the trend of populations on our coast. The assessments of the status of the criteria and of the element have thus been included in the results for the whole of ABI_PT_AA_AGCON_AG_CONTAC_ACON_AG_CONT_AG_CONT_AG_CONT_CONT_C, since it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848.
|
Assessment of the status of the species was based on the result of D1C2.
The reported information refers to the south-western and southern mainland of mainland Portugal (ABI_PT_AA_CONTAC_AG_CONTAC-AAG_CONTACT), since the information deemed most suitable for assessing its biomass is collected in the IPMA crustacean campaign, which takes place in these areas only. However, the species has a wider distribution, so it is expected that the information submitted and its assessments reflect the trend of populations on our coast. The assessments of the status of the criteria and of the element have thus been included in the results for the whole of ABI_PT_AA_AGCON_AG_CONTAC_ACON_AG_CONT_AG_CONT_AG_CONT_CONT_C, since it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848.
|
Assessment of the status of the species was based on the result of D1C2.
The reported information refers to the south-western and southern mainland of mainland Portugal (ABI_PT_AA_CONTAC_AG_CONTAC-AAG_CONTACT), since the information deemed most suitable for assessing its biomass is collected in the IPMA crustacean campaign, which takes place in these areas only. However, the species has a wider distribution, so it is expected that the information submitted and its assessments reflect the trend of populations on our coast. The assessments of the status of the criteria and of the element have thus been included in the results for the whole of ABI_PT_AA_AGCON_AG_CONTAC_ACON_AG_CONT_AG_CONT_AG_CONT_CONT_C, since it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848.
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
Assessment of the status of the species was based on the result of D1C2.
The information reported relates to the northern and south-western parts of the waters of mainland Portugal (ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CON_AG_CONT_B), where the species is preferably distributed. However, the assessments of the status of the criteria and of the element have been included in the results for the whole of ABI_PT_AA_AGCON_AG_CONTAC_ACON_AG_CONTAC_AG_CONT_AG_CONT_CONT_C, since it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848.
|
Assessment of the status of the species was based on the result of D1C2.
The information reported relates to the northern and south-western parts of the waters of mainland Portugal (ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CON_AG_CONT_B), where the species is preferably distributed. However, the assessments of the status of the criteria and of the element have been included in the results for the whole of ABI_PT_AA_AGCON_AG_CONTAC_ACON_AG_CONTAC_AG_CONT_AG_CONT_CONT_C, since it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848.
|
Assessment of the status of the species was based on the result of D1C2.
The information reported relates to the northern and south-western parts of the waters of mainland Portugal (ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CON_AG_CONT_B), where the species is preferably distributed. However, the assessments of the status of the criteria and of the element have been included in the results for the whole of ABI_PT_AA_AGCON_AG_CONTAC_ACON_AG_CONTAC_AG_CONT_AG_CONT_CONT_C, since it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848.
|
Assessment of the status of the species was based on the result of D1C2.
The reported information refers to the south-western and southern areas of mainland waters (ABI_PT_AAG_CONTAC-AG_AG_CONTAC-ACON_ACON_CON_C), since the information deemed most suitable for assessing its biomass is collected in the IPMA crustacean campaign, which takes place in these areas only. However, the assessments of the status of the criteria and of the element have been included in the results for the whole of ABI_PT_AA_AGCON_AG_CONTAC_ACON_AG_CONTAC_AG_CONT_AG_CONT_CONT_C, since it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848.
|
Assessment of the status of the species was based on the result of D1C2.
The reported information refers to the south-western and southern areas of mainland waters (ABI_PT_AAG_CONTAC-AG_AG_CONTAC-ACON_ACON_CON_C), since the information deemed most suitable for assessing its biomass is collected in the IPMA crustacean campaign, which takes place in these areas only. However, the assessments of the status of the criteria and of the element have been included in the results for the whole of ABI_PT_AA_AGCON_AG_CONTAC_ACON_AG_CONTAC_AG_CONT_AG_CONT_CONT_C, since it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848.
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
Assessment of the status of the species was based on the result of D1C2.
The species Lepidthrigla dieuzedei Blanc
|
Assessment of the status of the species was based on the result of D1C2.
The species Lepidthrigla dieuzedei Blanc
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
Assessment of the status of the species was based on the result of D1C2.
|
Assessment of the status of the species was based on the result of D1C2.
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
Assessment of the status of the species was based on the result of D1C2.
|
Assessment of the status of the species was based on the result of D1C2.
|
Assessment of the status of the species was based on the result of D1C2.
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
This item was considered in Descriptor 3.
The classification of each BEA stock was based on the integration of the assessment according to the values set for criteria D3C1 and D3C2.
The method of integration used for the assessment of Good Environmental Status (GES) was ?One All Outside? (OOAO). Thus, the overall assessment for each stock was classified in:
GES achieved, when both criteria (D3C1 and D3C2) were within the range defined for the reference values
|
Integration rule type parameter |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Integration rule description parameter |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Integration rule type criteria |
|||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Integration rule description criteria |
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
Only one criterion was assessed under Descriptor 1.
|
|||||||||||||||||||||||
GES extent threshold |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
75.00 |
|||||||||
GES extent achieved |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
100.00 |
|||||||||
GES extent unit |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
Proportion of species in good status within species group |
|||||||||
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
GES achieved |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Description overall status |
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The fish listed in Annexes II, IV and V of the Habitats Directive has not been included in the list because there is no data to characterise and assess their coastal components.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except P. erythrorinus, S. hepatus, S. cantharus, the evaluation area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The fish listed in Annexes II, IV and V of the Habitats Directive has not been included in the list because there is no data to characterise and assess their coastal components.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except P. erythrorinus, S. hepatus, S. cantharus, the evaluation area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The fish listed in Annexes II, IV and V of the Habitats Directive has not been included in the list because there is no data to characterise and assess their coastal components.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except P. erythrorinus, S. hepatus, S. cantharus, the evaluation area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The fish listed in Annexes II, IV and V of the Habitats Directive has not been included in the list because there is no data to characterise and assess their coastal components.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except P. erythrorinus, S. hepatus, S. cantharus, the evaluation area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The fish listed in Annexes II, IV and V of the Habitats Directive has not been included in the list because there is no data to characterise and assess their coastal components.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except P. erythrorinus, S. hepatus, S. cantharus, the evaluation area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The fish listed in Annexes II, IV and V of the Habitats Directive has not been included in the list because there is no data to characterise and assess their coastal components.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except P. erythrorinus, S. hepatus, S. cantharus, the evaluation area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The fish listed in Annexes II, IV and V of the Habitats Directive has not been included in the list because there is no data to characterise and assess their coastal components.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except P. erythrorinus, S. hepatus, S. cantharus, the evaluation area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The fish listed in Annexes II, IV and V of the Habitats Directive has not been included in the list because there is no data to characterise and assess their coastal components.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except P. erythrorinus, S. hepatus, S. cantharus, the evaluation area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The fish listed in Annexes II, IV and V of the Habitats Directive has not been included in the list because there is no data to characterise and assess their coastal components.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except P. erythrorinus, S. hepatus, S. cantharus, the evaluation area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The fish listed in Annexes II, IV and V of the Habitats Directive has not been included in the list because there is no data to characterise and assess their coastal components.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except P. erythrorinus, S. hepatus, S. cantharus, the evaluation area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The fish listed in Annexes II, IV and V of the Habitats Directive has not been included in the list because there is no data to characterise and assess their coastal components.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except P. erythrorinus, S. hepatus, S. cantharus, the evaluation area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The fish listed in Annexes II, IV and V of the Habitats Directive has not been included in the list because there is no data to characterise and assess their coastal components.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except P. erythrorinus, S. hepatus, S. cantharus, the evaluation area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The fish listed in Annexes II, IV and V of the Habitats Directive has not been included in the list because there is no data to characterise and assess their coastal components.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except P. erythrorinus, S. hepatus, S. cantharus, the evaluation area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The fish listed in Annexes II, IV and V of the Habitats Directive has not been included in the list because there is no data to characterise and assess their coastal components.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except P. erythrorinus, S. hepatus, S. cantharus, the evaluation area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
In the case of deep-sea fish, information was mainly used for the IPMA crustacean campaign, the series of which starts in 1997. This campaign takes place only in the south-western and southern parts of the continent (ABI_PT_AAG_CONTAC_AG_CONT_ACON_AG_CONT_B), so the reported information refers only to these areas. However, all species have a wider distribution and the information presented and their assessments are expected to reflect the population trend on our coast. The assessment of the status of each species has thus been integrated at the level of the whole Portuguese coast to assess GES, since all areas are considered to be ecologically relevant for this species group as proposed in Commission Decision (EU) 2017/848.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
In the case of deep-sea fish, information was mainly used for the IPMA crustacean campaign, the series of which starts in 1997. This campaign takes place only in the south-western and southern parts of the continent (ABI_PT_AAG_CONTAC_AG_CONT_ACON_AG_CONT_B), so the reported information refers only to these areas. However, all species have a wider distribution and the information presented and their assessments are expected to reflect the population trend on our coast. The assessment of the status of each species has thus been integrated at the level of the whole Portuguese coast to assess GES, since all areas are considered to be ecologically relevant for this species group as proposed in Commission Decision (EU) 2017/848.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
In the case of deep-sea fish, information was mainly used for the IPMA crustacean campaign, the series of which starts in 1997. This campaign takes place only in the south-western and southern parts of the continent (ABI_PT_AAG_CONTAC_AG_CONT_ACON_AG_CONT_B), so the reported information refers only to these areas. However, all species have a wider distribution and the information presented and their assessments are expected to reflect the population trend on our coast. The assessment of the status of each species has thus been integrated at the level of the whole Portuguese coast to assess GES, since all areas are considered to be ecologically relevant for this species group as proposed in Commission Decision (EU) 2017/848.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
In the case of deep-sea fish, information was mainly used for the IPMA crustacean campaign, the series of which starts in 1997. This campaign takes place only in the south-western and southern parts of the continent (ABI_PT_AAG_CONTAC_AG_CONT_ACON_AG_CONT_B), so the reported information refers only to these areas. However, all species have a wider distribution and the information presented and their assessments are expected to reflect the population trend on our coast. The assessment of the status of each species has thus been integrated at the level of the whole Portuguese coast to assess GES, since all areas are considered to be ecologically relevant for this species group as proposed in Commission Decision (EU) 2017/848.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
In the case of deep-sea fish, information was mainly used for the IPMA crustacean campaign, the series of which starts in 1997. This campaign takes place only in the south-western and southern parts of the continent (ABI_PT_AAG_CONTAC_AG_CONT_ACON_AG_CONT_B), so the reported information refers only to these areas. However, all species have a wider distribution and the information presented and their assessments are expected to reflect the population trend on our coast. The assessment of the status of each species has thus been integrated at the level of the whole Portuguese coast to assess GES, since all areas are considered to be ecologically relevant for this species group as proposed in Commission Decision (EU) 2017/848.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
In the case of deep-sea fish, information was mainly used for the IPMA crustacean campaign, the series of which starts in 1997. This campaign takes place only in the south-western and southern parts of the continent (ABI_PT_AAG_CONTAC_AG_CONT_ACON_AG_CONT_B), so the reported information refers only to these areas. However, all species have a wider distribution and the information presented and their assessments are expected to reflect the population trend on our coast. The assessment of the status of each species has thus been integrated at the level of the whole Portuguese coast to assess GES, since all areas are considered to be ecologically relevant for this species group as proposed in Commission Decision (EU) 2017/848.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
In the case of deep-sea fish, information was mainly used for the IPMA crustacean campaign, the series of which starts in 1997. This campaign takes place only in the south-western and southern parts of the continent (ABI_PT_AAG_CONTAC_AG_CONT_ACON_AG_CONT_B), so the reported information refers only to these areas. However, all species have a wider distribution and the information presented and their assessments are expected to reflect the population trend on our coast. The assessment of the status of each species has thus been integrated at the level of the whole Portuguese coast to assess GES, since all areas are considered to be ecologically relevant for this species group as proposed in Commission Decision (EU) 2017/848.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
In the case of deep-sea fish, information was mainly used for the IPMA crustacean campaign, the series of which starts in 1997. This campaign takes place only in the south-western and southern parts of the continent (ABI_PT_AAG_CONTAC_AG_CONT_ACON_AG_CONT_B), so the reported information refers only to these areas. However, all species have a wider distribution and the information presented and their assessments are expected to reflect the population trend on our coast. The assessment of the status of each species has thus been integrated at the level of the whole Portuguese coast to assess GES, since all areas are considered to be ecologically relevant for this species group as proposed in Commission Decision (EU) 2017/848.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
In the case of deep-sea fish, information was mainly used for the IPMA crustacean campaign, the series of which starts in 1997. This campaign takes place only in the south-western and southern parts of the continent (ABI_PT_AAG_CONTAC_AG_CONT_ACON_AG_CONT_B), so the reported information refers only to these areas. However, all species have a wider distribution and the information presented and their assessments are expected to reflect the population trend on our coast. The assessment of the status of each species has thus been integrated at the level of the whole Portuguese coast to assess GES, since all areas are considered to be ecologically relevant for this species group as proposed in Commission Decision (EU) 2017/848.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
In the case of deep-sea fish, information was mainly used for the IPMA crustacean campaign, the series of which starts in 1997. This campaign takes place only in the south-western and southern parts of the continent (ABI_PT_AAG_CONTAC_AG_CONT_ACON_AG_CONT_B), so the reported information refers only to these areas. However, all species have a wider distribution and the information presented and their assessments are expected to reflect the population trend on our coast. The assessment of the status of each species has thus been integrated at the level of the whole Portuguese coast to assess GES, since all areas are considered to be ecologically relevant for this species group as proposed in Commission Decision (EU) 2017/848.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
In the case of deep-sea fish, information was mainly used for the IPMA crustacean campaign, the series of which starts in 1997. This campaign takes place only in the south-western and southern parts of the continent (ABI_PT_AAG_CONTAC_AG_CONT_ACON_AG_CONT_B), so the reported information refers only to these areas. However, all species have a wider distribution and the information presented and their assessments are expected to reflect the population trend on our coast. The assessment of the status of each species has thus been integrated at the level of the whole Portuguese coast to assess GES, since all areas are considered to be ecologically relevant for this species group as proposed in Commission Decision (EU) 2017/848.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
In the case of deep-sea fish, information was mainly used for the IPMA crustacean campaign, the series of which starts in 1997. This campaign takes place only in the south-western and southern parts of the continent (ABI_PT_AAG_CONTAC_AG_CONT_ACON_AG_CONT_B), so the reported information refers only to these areas. However, all species have a wider distribution and the information presented and their assessments are expected to reflect the population trend on our coast. The assessment of the status of each species has thus been integrated at the level of the whole Portuguese coast to assess GES, since all areas are considered to be ecologically relevant for this species group as proposed in Commission Decision (EU) 2017/848.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. For the calculation of the ratio only the species with assessment were considered.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species except A. sphyraena, G. argenteus, Lepidtrimla spp., the assessment area coincides with their respective (preferred) distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. In this particular case, only 2 species were assessed for pelagic fish and for this reason no integration of information and subsequent assessment of the GES of this species group has been carried out.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species, the assessment area coincides with its distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. In this particular case, only 2 species were assessed for pelagic fish and for this reason no integration of information and subsequent assessment of the GES of this species group has been carried out.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species, the assessment area coincides with its distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. In this particular case, only 2 species were assessed for pelagic fish and for this reason no integration of information and subsequent assessment of the GES of this species group has been carried out.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species, the assessment area coincides with its distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. In this particular case, only 2 species were assessed for pelagic fish and for this reason no integration of information and subsequent assessment of the GES of this species group has been carried out.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species, the assessment area coincides with its distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. In this particular case, only 2 species were assessed for pelagic fish and for this reason no integration of information and subsequent assessment of the GES of this species group has been carried out.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species, the assessment area coincides with its distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. In this particular case, only 2 species were assessed for pelagic fish and for this reason no integration of information and subsequent assessment of the GES of this species group has been carried out.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species, the assessment area coincides with its distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. In this particular case, only 2 species were assessed for pelagic fish and for this reason no integration of information and subsequent assessment of the GES of this species group has been carried out.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species, the assessment area coincides with its distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. In this particular case, only 2 species were assessed for pelagic fish and for this reason no integration of information and subsequent assessment of the GES of this species group has been carried out.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species, the assessment area coincides with its distribution area in national waters.
|
GES was integrated at the level of the species group only when the estimated number of species was equal or higher than 3. In this particular case, only 2 species were assessed for pelagic fish and for this reason no integration of information and subsequent assessment of the GES of this species group has been carried out.
The GES assessment has been carried out for all ABI_PT_AA_CONTAC_AG_CONTAC_ACON_AG_CONT_AG_CONTAC_ACONF_CONTIN_C areas, because it is considered that this is the environmentally relevant scale for this species group as proposed in Commission Decision (EU) 2017/848. In this case, and for all species, the assessment area coincides with its distribution area in national waters.
|
Assessments period |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
2012-2017 |
Related pressures |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Related targets |
|
|
|
|
|
|
|
|
|