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
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Changes to hydrological conditions
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Changes to hydrological conditions
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Changes to hydrological conditions
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Changes to hydrological conditions
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Changes to hydrological conditions
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Changes to hydrological conditions
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Changes to hydrological conditions
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Changes to hydrological conditions
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Changes to hydrological conditions
  • Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
Related targets
  • ABIPT-T6-D1Cont
  • ABIPT-T6-D1Cont
  • ABIPT-T6-D1Cont
  • ABIPT-T6-D1Cont
  • ABIPT-T6-D1Cont
  • ABIPT-T6-D1Cont
  • ABIPT-T6-D1Cont
  • ABIPT-T6-D1Cont
  • ABIPT-T6-D1Cont