Member State report / Art8 / 2018 / D1-C / 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 Cephalopods |
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-C
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Feature |
Coastal/shelf cephalopods
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Deep-sea cephalopods
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Element |
Alloteuthis spp. |
Loligo vulgaris |
Octopus vulgaris |
Sepia officinalis |
Eledone cirrhosa |
Illex coindetii |
Todaropsis eblanae |
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Element code |
138138 |
140271 |
140605 |
141444 |
140600 |
140621 |
140625 |
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Element code source |
Species (D1) http://www.marinespecies.org/
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Species (D1) http://www.marinespecies.org/
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Species (D1) http://www.marinespecies.org/
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Species (D1) http://www.marinespecies.org/
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Species (D1) http://www.marinespecies.org/
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Species (D1) http://www.marinespecies.org/
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Species (D1) http://www.marinespecies.org/
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Element 2 |
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Element 2 code |
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Element 2 code source |
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Element source |
National |
National |
National |
National |
National |
National |
National |
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Criterion |
D1C1
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D1C2
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D1C3
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D1C1
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D1C2
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D1C3
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D1C1
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D1C2
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D1C3
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D1C1
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D1C2
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D1C3
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Parameter |
Biomass
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Other
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Biomass
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Other
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Biomass
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Other
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Biomass
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Other
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Parameter other |
L95
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L95
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L95
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L95
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Threshold value upper |
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Threshold value lower |
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Threshold qualitative |
Combination of break-point analysis with trend over the last 5 years (Probst and Steelzenmuller, 2015 method)
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Combination of break-point analysis with trend over the last 5 years (Probst and Steelzenmuller, 2015 method)
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Combination of break-point analysis with trend over the last 5 years (Probst and Steelzenmuller, 2015 method)
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Combination of break-point analysis with trend over the last 5 years (Probst and Steelzenmuller, 2015 method)
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Threshold value source |
Other (specify)
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Other (specify)
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Other (specify)
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Other (specify)
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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. |
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Value achieved upper |
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Value achieved lower |
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Value unit |
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Value unit other |
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Proportion threshold value |
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Proportion value achieved |
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Proportion threshold value unit |
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Trend |
Deteriorating |
Stable |
Improving |
Deteriorating |
Improving |
Stable |
Improving |
Improving |
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Parameter achieved |
No |
Not assessed |
Yes |
Not assessed |
Yes |
Not assessed |
Yes |
Not assessed |
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Description parameter |
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 below the estimated average for the reference period (1.34 and 1.52), respectively), althou...
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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 resp...
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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 resp...
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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 (0.36 and 1.40, respectively),...
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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 resp...
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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 resp...
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Related indicator |
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Criteria status |
Not assessed |
Not good |
Not assessed |
Not assessed |
Good |
Not assessed |
Not assessed |
Good |
Not assessed |
Not assessed |
Good |
Not assessed |
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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 pro...
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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 pro...
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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 pro...
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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 pro...
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Element status |
Not good |
Not assessed |
Not assessed |
Not assessed |
Good |
Good |
Good |
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Description element |
Includes the species Allowits subticulata (Lamarck, 1798) and Allosuthis media (Linnaeus, 1758). Species have been combined with gender due to identification problems in the initial years of the series.
Assessment of the status of the species was based on the result of D1C2.
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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)....
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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)....
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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)....
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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 ...
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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 ...
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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 ...
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Integration rule type parameter |
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Integration rule description parameter |
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Integration rule type criteria |
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Integration rule description criteria |
Only one criterion was assessed.
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GES extent threshold |
75.00 |
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GES extent achieved |
100.00 |
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GES extent unit |
Proportion of species in good status within species group |
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GES achieved |
Not assessed |
GES achieved |
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Description overall status |
The information was considered insufficient to characterise and assess the different criteria for the species in this group. Given that only one species was evaluated, it was considered that it was not appropriate to integrate the results at the level of the group and, therefore, to assess GES.
...
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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 cephalopods, information has been used in the IPMA crustacean camp...
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Assessments period |
2012-2017 |
2012-2017 |
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Related pressures |
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Related targets |