Member State report / Art8 / 2018 / D1-R / Portugal / NE Atlantic: Macaronesia
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 Reptiles |
Member State | Portugal |
Region/subregion | NE Atlantic: Macaronesia |
Reported by | DGRM |
Report date | 2021-03-03 |
Report access | ART8_GES_PT_setembro2020.xml |
Azores Subdivision (AMA-PT-SD-AZO)
GES component |
D1-R
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Feature |
Turtles
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Element |
Caretta caretta |
Chelonia mydas |
Dermochelys coriacea |
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Element code |
137205 |
137206 |
137209 |
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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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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 |
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Criterion |
D1C1
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D1C2
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D1C3
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D1C4
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D1C5
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D1C1
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D1C2
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D1C3
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D1C4
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D1C5
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D1C1
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D1C2
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D1C3
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D1C4
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D1C5
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Parameter |
Abundance
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Other
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Parameter other |
The Body Condition Index (BCI)
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Threshold value upper |
1.76 |
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Threshold value lower |
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Threshold qualitative |
The trend in the abundance of turtles is not adversely affected.
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Threshold value source |
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Threshold value source other |
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Value achieved upper |
1.82 |
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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 |
Stable |
Unknown |
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Parameter achieved |
Yes, based on low risk |
Unknown |
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Description parameter |
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Related indicator |
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Criteria status |
Unknown |
Good, based on low risk |
Unknown |
Not assessed |
Not assessed |
Unknown |
Unknown |
Unknown |
Not assessed |
Not assessed |
Unknown |
Unknown |
Unknown |
Not assessed |
Not assessed |
Description criteria |
AMA-ST-BYC-MR ? SeaTurtlesBycatch: The accidental catch data for the Portuguese longline fleet operating in the waters of the Azores shall intermittently compile as from 2008. Since 2015, the Azores fisheries have been continuously monitored as part of the COSTA project (Consolidating Sea Turtle ...
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AMA-ST-ABU-DS ? SeaTurtlesAbdateDistress: 46 turtles together were found during the OPIC SECO II ocean campaign campaign. The number of sightings of turtles did not allow the spatial analysis to be carried out for the calculation of the abundance in the Azores and, therefore, only an estimate is made on the basis of the experimental design. Total abundance estimation is 5.187 (95 % JI
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AMA-PT-Z_DEM_BCI ? SeaTurtlesBodyConditionIndex
Corporate Condition Index (BCI)
The demographic parameter of the population considered for assessing sea turtles under this criterion is the Body Condition Index. This characteristic provides information on health and pressures affecting the popula...
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The distribution area is a primary criterion for sea turtles (Commission Decision (EU) 2017/848, 2017). This criterion is not considered appropriate for oceanic sea turtles which demonstrate broad distribution limits and only a fraction of their distribution is included within areas under nationa...
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Habitat for species is a primary criterion for sea turtles (Commission Decision (EU) 2017/848, 2017). This criterion is not considered appropriate for ocean turtles. Only a fraction of its habitat is included in areas under the jurisdiction of the countries of the European Union and generally occ...
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D1C1 By-catch mortality rate (BR ? bycatch rate)
The mortality rate by acccess is a primary criterion for sea turtles (Commission Directive 2017/845/EC, 2017). Incidental catching by fishing is one of the main anthropogenic pressures affecting sea turtle populations, which is one of the main caus...
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The abundance of the population is a primary criterion for sea turtles (Commission Decision (EU) 2017/848, 2017). Juvenile turtles form groupings in the archipelagos of Macaronesia, but these animals originate from American and African spawning beaches. The variation in hatching success has an in...
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D1C3 Population demographics
Demographic characteristics of the population are a secondary criterion for sea turtles (Commission Decision (EU) 2017/848, 2017).
Corporate Condition Index (BCI)
The demographic parameter of the population considered for assessing sea turtles under this criterion is ...
|
The distribution area is a primary criterion for sea turtles (Commission Decision (EU) 2017/848, 2017). This criterion is not considered appropriate for oceanic sea turtles which demonstrate broad distribution limits and only a fraction of their distribution is included within areas under nationa...
|
Habitat for species is a primary criterion for sea turtles (Commission Decision (EU) 2017/848, 2017). This criterion is not considered appropriate for ocean turtles. Only a fraction of its habitat is included in areas under the jurisdiction of the countries of the European Union and generally occ...
|
D1C1 By-catch mortality rate (BR ? bycatch rate)
The mortality rate by acccess is a primary criterion for sea turtles (Commission Directive 2017/845/EC, 2017). Incidental catching by fishing is one of the main anthropogenic pressures affecting sea turtle populations, which is one of the main caus...
|
The abundance of the population is a primary criterion for sea turtles (Commission Decision (EU) 2017/848, 2017). Juvenile turtles form groupings in the archipelagos of Macaronesia, but these animals originate from American and African spawning beaches. The variation in hatching success has an in...
|
D1C3 Population demographics
Demographic characteristics of the population are a secondary criterion for sea turtles (Commission Decision (EU) 2017/848, 2017).
Corporate Condition Index (BCI)
The demographic parameter of the population considered for assessing sea turtles under this criterion is ...
|
The distribution area is a primary criterion for sea turtles (Commission Decision (EU) 2017/848, 2017). This criterion is not considered appropriate for oceanic sea turtles which demonstrate broad distribution limits and only a fraction of their distribution is included within areas under nationa...
|
Habitat for species is a primary criterion for sea turtles (Commission Decision (EU) 2017/848, 2017). This criterion is not considered appropriate for ocean turtles. Only a fraction of its habitat is included in areas under the jurisdiction of the countries of the European Union and generally occ...
|
Element status |
Unknown |
Unknown |
Unknown |
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Description element |
An assessment of GES is not yet possible for the aggregation of the common loggerhead of the Azores as there is not sufficient information available for all criteria.
Only D1C2 was assessed. The information was considered insufficient to characterise and assess D1C1 and D1C3 in this cycle and i...
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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 |
For assessment and integration of environmental status it is essential to collect a wider/diverse set of data, filling gaps for a precision assessment. the suggested integration rule OOAO (WG BEA, 2017) could offer a reliable and robust integration method if the status of each element, criterion, indicator could be assessed with a very high degree of confidence, this is rarely the case.
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GES extent threshold |
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GES extent achieved |
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GES extent unit |
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GES achieved |
Unknown |
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Description overall status |
Only D1C2 has been assessed for one item. The information was considered insufficient to characterise and assess D1C1 and D1C3 in this cycle and in those cases GES was classified as ?Unknown?. Criteria D1C4 and D1C5 considered to be unsuitable, taking into account the characteristics of this func...
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Assessments period |
2012-2018 |
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Related pressures |
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Related targets |
Madeira subdivision (AMA-PT-SD-MAD)
GES component |
D1-R
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Feature |
Turtles
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Element |
Caretta caretta |
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Element code |
137205 |
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Element code source |
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 |
MS in (sub)region |
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Criterion |
D1C1
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D1C2
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D1C3
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Parameter |
Mortality rate / Mortality rate from fishing (F)
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Abundance
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Other
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Parameter other |
The Body condition index
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Threshold value upper |
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Threshold value lower |
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Threshold qualitative |
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Threshold value source |
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Threshold value source other |
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Value achieved upper |
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Value achieved lower |
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Value unit |
(number of) individuals
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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 |
Unknown |
Unknown |
Unknown |
Parameter achieved |
Not assessed |
Not assessed |
Not assessed |
Description parameter |
Based on experimental design abundance: 149 individuals (95 % CI
|
1,74 ± 0,08 (n = 7) [2017; MISTIC SEAS II]
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Related indicator |
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Criteria status |
Not assessed |
Not assessed |
Not assessed |
Description criteria |
The mortality rate by accessibilities of the common turtles has not yet been assessed in Madeira.
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This is the first estimate of abundance of sea turtles in Madeira and therefore established as a reference value for future evaluations.
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In order to be able to assess the GES in a reliable manner, further sampling is necessary and the threshold and the reference value must be defined.
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Element status |
Not assessed |
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Description element |
An assessment of GES is not yet available for the whole common turtle aggregation in Madeira
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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 |
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GES extent threshold |
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GES extent achieved |
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GES extent unit |
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GES achieved |
Not assessed |
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Description overall status |
Sea turtles are highly mobile with an extension of distribution that is not limited to the waters of Macaronesia.
In Madeira there are no current abundance estimates for common loggerhead turtles. The global sex ratio of the common loggerhead, calculated between 2000 and 2006 in Madeira, was 2 fe...
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Assessments period |
2014-2018 |
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Related pressures |
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Related targets |
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