Member State report / Art8 / 2018 / D1-B / Spain / Mediterranean: Western Mediterranean Sea
Report type | Member State report to Commission |
MSFD Article | Art. 8 Initial assessment (and Art. 17 updates) |
Report due | 2018-10-15 |
GES Descriptor | D1 Birds |
Member State | Spain |
Region/subregion | Mediterranean: Western Mediterranean Sea |
Reported by | Subdirección General para la protección del mar. D.G. Sostenibilidad de la Costa y del Mar. Minister |
Report date | 2020-02-03 |
Report access | msfd2018-ART8GES_MOD2020.xml |
Demarcación marina del Estrecho y Alborán (MWE-ES-SD-ESAL)
GES component |
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Feature |
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Element |
Puffinus mauretanicus |
Puffinus mauretanicus |
Puffinus mauretanicus |
Puffinus mauretanicus |
Puffinus mauretanicus |
Calonectris diomedea borealis |
Calonectris diomedea borealis |
Calonectris diomedea borealis |
Calonectris diomedea borealis |
Calonectris diomedea borealis |
Calonectris diomedea borealis |
Calonectris diomedea diomedea |
Calonectris diomedea diomedea |
Calonectris diomedea diomedea |
Calonectris diomedea diomedea |
Calonectris diomedea diomedea |
Calonectris diomedea diomedea |
Larus audouinii |
Larus audouinii |
Larus audouinii |
Larus audouinii |
Larus audouinii |
Larus audouinii |
Element code |
445503 |
445503 |
445503 |
445503 |
445503 |
226024 |
226024 |
226024 |
226024 |
226024 |
226024 |
226017 |
226017 |
226017 |
226017 |
226017 |
226017 |
137139 |
137139 |
137139 |
137139 |
137139 |
137139 |
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/
|
Element 2 |
|||||||||||||||||||||||
Element 2 code |
|||||||||||||||||||||||
Element 2 code source |
|||||||||||||||||||||||
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 |
Criterion |
D1C1
|
D1C2
|
D1C3
|
D1C4
|
D1C5
|
D1C1
|
D1C2
|
D1C3
|
D1C3
|
D1C4
|
D1C5
|
D1C1
|
D1C2
|
D1C3
|
D1C3
|
D1C4
|
D1C5
|
D1C1
|
D1C2
|
D1C3
|
D1C3
|
D1C4
|
D1C5
|
Parameter |
Mortality rate / Mortality rate from fishing (F)
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Other
|
Survival rate
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Other
|
Survival rate
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Other
|
Survival rate
|
||||||||||
Parameter other |
Breeding success
|
Breeding success
|
Breeding success
|
||||||||||||||||||||
Threshold value upper |
0.3 |
0.9 |
0.3 |
0.9 |
2478.0 |
0.3 |
0.9 |
||||||||||||||||
Threshold value lower |
|||||||||||||||||||||||
Threshold qualitative |
By-catch should "approach zero". Assessment by expert criteria. |
By-catch should "approach zero". Assessment by expert criteria. |
By-catch should "approach zero". Assessment by expert criteria. |
By-catch should "approach zero". Assessment by expert criteria. |
|||||||||||||||||||
Threshold value source |
Other (specify)
|
Other (specify)
|
OSPAR Convention
|
OSPAR Convention
|
Other (specify)
|
Other (specify)
|
OSPAR Convention
|
OSPAR Convention
|
Other (specify)
|
Other (specify)
|
OSPAR Convention
|
Other (specify)
|
|||||||||||
Threshold value source other |
Expert criteria
|
Expert criteria
|
Expert criteria
|
Regional (OSPAR, addapted under expert criteria)
|
Expert criteria
|
Regional (OSPAR, addapted under expert criteria)
|
Regional (OSPAR, addapted under expert criteria)
|
||||||||||||||||
Value achieved upper |
1749.0 |
||||||||||||||||||||||
Value achieved lower |
|||||||||||||||||||||||
Value unit |
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
||||||||||
Value unit other |
birds/1000 hoks (longline)
|
birds/1000 hoks (longline)
|
Breeding pairs
|
fledged Chicks per pair
|
TRAIN
|
birds/1000 hoks (longline)
|
Breeding pairs
|
fledged Chicks per pair
|
TRAIN
|
birds/1000 hoks (longline)
|
Breeding pairs
|
fledged Chicks per pair
|
TRAIN
|
||||||||||
Proportion threshold value |
|||||||||||||||||||||||
Proportion value achieved |
|||||||||||||||||||||||
Proportion threshold value unit |
|||||||||||||||||||||||
Trend |
Unknown |
Unknown |
Stable |
Unknown |
Unknown |
Unknown |
Stable |
Unknown |
Unknown |
Unknown |
Deteriorating |
Stable |
Deteriorating |
||||||||||
Parameter achieved |
Unknown |
No |
Unknown |
Unknown |
Unknown |
No |
Unknown |
Unknown |
Unknown |
Unknown |
No |
Yes |
No |
||||||||||
Description parameter |
PRECAUTIONARY
|
PRECAUTIONARY
|
Isla de Alborán: 0.32
|
<0.9
|
|||||||||||||||||||
Related indicator |
|||||||||||||||||||||||
Criteria status |
Unknown |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not good |
Unknown |
Unknown |
Unknown |
Not assessed |
Not assessed |
Not good |
Unknown |
Unknown |
Unknown |
Not assessed |
Not assessed |
Unknown |
Not good |
Unknown |
Unknown |
Not assessed |
Not assessed |
Description criteria |
|||||||||||||||||||||||
Element status |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Description element |
|||||||||||||||||||||||
Integration rule type parameter |
|||||||||||||||||||||||
Integration rule description parameter |
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
Integration rule type criteria |
|||||||||||||||||||||||
Integration rule description criteria |
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
GES extent threshold |
|||||||||||||||||||||||
GES extent achieved |
|||||||||||||||||||||||
GES extent unit |
|||||||||||||||||||||||
GES achieved |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Description overall status |
|||||||||||||||||||||||
Assessments period |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
Related pressures |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Related targets |
|
|
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|
|
Demarcación marina levantino-balear (MWE-ES-SD-LEV)
GES component |
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
D1-B
|
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Feature |
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Pelagic-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Surface-feeding birds
|
Element |
Phalacrocorax aristotelis |
Phalacrocorax aristotelis |
Phalacrocorax aristotelis |
Phalacrocorax aristotelis |
Phalacrocorax aristotelis |
Phalacrocorax aristotelis |
Puffinus mauretanicus |
Puffinus mauretanicus |
Puffinus mauretanicus |
Puffinus mauretanicus |
Puffinus mauretanicus |
Puffinus mauretanicus |
Calonectris diomedea diomedea |
Calonectris diomedea diomedea |
Calonectris diomedea diomedea |
Calonectris diomedea diomedea |
Calonectris diomedea diomedea |
Calonectris diomedea diomedea |
Hydrobates pelagicus |
Hydrobates pelagicus |
Hydrobates pelagicus |
Hydrobates pelagicus |
Hydrobates pelagicus |
Hydrobates pelagicus |
Larus audouinii |
Larus audouinii |
Larus audouinii |
Larus audouinii |
Larus audouinii |
Larus audouinii |
Sterna hirundo |
Sterna hirundo |
Sterna hirundo |
Sterna hirundo |
Sterna hirundo |
Sterna sandvicensis |
Sterna sandvicensis |
Sterna sandvicensis |
Sterna sandvicensis |
Sterna sandvicensis |
Sternula albifrons |
Sternula albifrons |
Sternula albifrons |
Sternula albifrons |
Sternula albifrons |
Element code |
137178 |
137178 |
137178 |
137178 |
137178 |
137178 |
445503 |
445503 |
445503 |
445503 |
445503 |
445503 |
226017 |
226017 |
226017 |
226017 |
226017 |
226017 |
137189 |
137189 |
137189 |
137189 |
137189 |
137189 |
137139 |
137139 |
137139 |
137139 |
137139 |
137139 |
137162 |
137162 |
137162 |
137162 |
137162 |
137166 |
137166 |
137166 |
137166 |
137166 |
567480 |
567480 |
567480 |
567480 |
567480 |
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/
|
Element 2 |
|||||||||||||||||||||||||||||||||||||||||||||
Element 2 code |
|||||||||||||||||||||||||||||||||||||||||||||
Element 2 code source |
|||||||||||||||||||||||||||||||||||||||||||||
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 |
Criterion |
D1C1
|
D1C2
|
D1C3
|
D1C3
|
D1C4
|
D1C5
|
D1C1
|
D1C2
|
D1C3
|
D1C3
|
D1C4
|
D1C5
|
D1C1
|
D1C2
|
D1C3
|
D1C3
|
D1C4
|
D1C5
|
D1C1
|
D1C2
|
D1C3
|
D1C3
|
D1C4
|
D1C5
|
D1C1
|
D1C2
|
D1C3
|
D1C3
|
D1C4
|
D1C5
|
D1C1
|
D1C2
|
D1C3
|
D1C4
|
D1C5
|
D1C1
|
D1C2
|
D1C3
|
D1C4
|
D1C5
|
D1C1
|
D1C2
|
D1C3
|
D1C4
|
D1C5
|
Parameter |
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Other
|
Survival rate
|
Distribution (spatial)
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Other
|
Survival rate
|
Distribution (spatial)
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Other
|
Survival rate
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Other
|
Survival rate
|
Mortality rate / Mortality rate from fishing (F)
|
Abundance
|
Other
|
Survival rate
|
Abundance
|
Other
|
Abundance
|
Other
|
Abundance
|
Other
|
|||||||||||||||||
Parameter other |
breeding succes
|
breeding succes
|
Breeding success
|
Breeding success
|
Breeding success
|
Breeding success
|
Breeding success
|
Breeding success
|
|||||||||||||||||||||||||||||||||||||
Threshold value upper |
1.2 |
0.8 |
0.3 |
0.9 |
0.3 |
0.9 |
0.3 |
0.9 |
11880.0 |
0.3 |
0.9 |
4475.0 |
0.99 |
3178.0 |
0.99 |
869.0 |
0.99 |
||||||||||||||||||||||||||||
Threshold value lower |
|||||||||||||||||||||||||||||||||||||||||||||
Threshold qualitative |
By-catch should "approach zero". Assessment by expert criteria. |
By-catch should "approach zero". Assessment by expert criteria. |
By-catch should "approach zero". Assessment by expert criteria. |
By-catch should "approach zero". Assessment by expert criteria. |
By-catch should "approach zero". Assessment by expert criteria. |
||||||||||||||||||||||||||||||||||||||||
Threshold value source |
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
OSPAR Convention
|
OSPAR Convention
|
Other (specify)
|
Other (specify)
|
OSPAR Convention
|
OSPAR Convention
|
Other (specify)
|
Other (specify)
|
OSPAR Convention
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
Other (specify)
|
OSPAR Convention
|
Other (specify)
|
OSPAR Convention
|
||||||||||||||||||||||
Threshold value source other |
Expert criteria
|
Regional (OSPAR, addapted under expert criteria)
|
Regional (OSPAR, addapted under expert criteria)
|
Expert criteria
|
Regional (OSPAR, addapted under expert criteria)
|
Regional (OSPAR, addapted under expert criteria)
|
Expert criteria
|
Expert criteria
|
Regional (OSPAR, addapted under expert criteria)
|
Expert criteria
|
Regional (OSPAR, addapted under expert criteria)
|
Regional (OSPAR, addapted under expert criteria)
|
Regional (OSPAR, addapted under expert criteria)
|
Regional (OSPAR, addapted under expert criteria)
|
Regional (OSPAR, addapted under expert criteria)
|
Regional (OSPAR, addapted under expert criteria)
|
|||||||||||||||||||||||||||||
Value achieved upper |
2.0 |
3.75 |
0.8 |
0.81 |
0.43 |
13164.0 |
2.6 |
6277.0 |
3578.0 |
935.0 |
|||||||||||||||||||||||||||||||||||
Value achieved lower |
1.17 |
0.12 |
0.59 |
0.81 |
0.17 |
0.27 |
|||||||||||||||||||||||||||||||||||||||
Value unit |
Other
|
(number of) individuals
|
Other
|
Other
|
Other
|
(number of) individuals
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
|||||||||||||||||||
Value unit other |
fragmentation information
|
fledged Chicks per pair
|
survival rate
|
birds/1000 hoks (longline)
|
fledged Chicks per pair
|
survival rate
|
birds/1000 hooks (DEMERSAL longline)
|
Breeding pairs
|
fledged Chicks per pair
|
TRAIN
|
birds/1000 hoks (longline)
|
Breeding pairs
|
fledged Chicks per pair
|
TRAIN
|
birds/1000 hoks (longline)
|
Breeding pairs
|
fledged Chicks per pair
|
TRAIN
|
Breeding pairs
|
fledged Chicks per pair
|
Breeding pairs
|
fledged Chicks per pair
|
Breeding pairs
|
fledged Chicks per pair
|
|||||||||||||||||||||
Proportion threshold value |
|||||||||||||||||||||||||||||||||||||||||||||
Proportion value achieved |
|||||||||||||||||||||||||||||||||||||||||||||
Proportion threshold value unit |
|||||||||||||||||||||||||||||||||||||||||||||
Trend |
Unknown |
Unknown |
Stable |
Unknown |
Unknown |
Unknown |
Unknown |
Stable |
Deteriorating |
Unknown |
Unknown |
Unknown |
Stable |
Deteriorating |
Unknown |
Stable |
Unknown |
Unknown |
Unknown |
Deteriorating |
Stable |
Deteriorating |
Stable |
Unknown |
Stable |
Unknown |
Stable |
Unknown |
|||||||||||||||||
Parameter achieved |
No |
Unknown |
Yes |
Unknown |
Unknown |
No |
Unknown |
Yes |
No |
Unknown |
No |
No |
Yes |
No |
No |
Unknown |
Unknown |
Unknown |
Unknown |
No |
Yes |
No |
Yes |
Unknown |
Yes |
Unknown |
Yes |
Unknown |
|||||||||||||||||
Description parameter |
Columbretes: 60 Pantaleu: 200
|
Pantaleu: 0.69
Columbretes: 0.62
|
Pantaleu: 0.87
Columbretes: 0.71
|
PRECAUTIONARY
|
especie claramente está en declive porque lleva descendiendo sin parar su población en los últimos 10 años, sin embargo la mediana de 2012-2017 aún no ha llegado al umbral marcado del 70% de la mediana máxima para un periodo de 6 años
|
.
|
<0.9
|
.
|
.
|
.
|
|||||||||||||||||||||||||||||||||||
Related indicator |
|
|
|||||||||||||||||||||||||||||||||||||||||||
Criteria status |
Not good |
Unknown |
Unknown |
Unknown |
Unknown |
Not assessed |
Not good |
Unknown |
Unknown |
Unknown |
Unknown |
Not assessed |
Not good |
Not good |
Unknown |
Unknown |
Not assessed |
Not assessed |
Not assessed |
Good |
Unknown |
Unknown |
Not assessed |
Not assessed |
Unknown |
Not good |
Unknown |
Unknown |
Not assessed |
Not assessed |
Not assessed |
Good |
Unknown |
Not assessed |
Not assessed |
Not assessed |
Good |
Unknown |
Not assessed |
Not assessed |
Not assessed |
Good |
Unknown |
Not assessed |
Not assessed |
Description criteria |
No (precautionary)
|
Los pocos datos disponibles en la actualidad parecen sugerir que se dan capturas accidentales o bien son excepcionales, por lo que esta presión no tendría un impacto significativo en la especie.
|
Los Procellariiformes son especies longevas y muy filopátricas, por lo que no se llega a la desaparición de una colonia hasta una fase ya muy avanzada de un declive. En este sentido, se pueden
medir otras variables que permiten detectar problemas de conservación de forma mucho más prematura, especialmente relativos a parámetros reproductivos. Dado que éstos se incluyen en
el Criterio D1C3, se considera que el presente criterio solo aportaría información redundante y que además llegaría demasiado tarde para desplegar medidas de gestión eficaces. Por este motivo,
se deja el Criterio D1C4 fuera de esta evaluación.
|
||||||||||||||||||||||||||||||||||||||||||
Element status |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not assessed |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Not good |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Good |
Description element |
|||||||||||||||||||||||||||||||||||||||||||||
Integration rule type parameter |
|||||||||||||||||||||||||||||||||||||||||||||
Integration rule description parameter |
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
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When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
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When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
|
When there is information from different colonies or sub-populations for the same species, within a marine demarcation, the representativeness of each enclave has been assessed when integrating, based on expert criteria. As a precaution, whenever an enclave considered as important for a certain species presents a negative BEA, a negative BEA is defined at marine demarcation level, even if in other enclaves the situation seems more favourable. However, if the enclave evaluated negatively is considered marginal and/or not very representative, the species can be evaluated with a positive BEA if it is defined as such in other enclaves. In cases of doubt, the evaluation of the OAB has been left in "amber" (i.e., as a precaution it is considered that the OAB is not reached, although the situation is not clearly unfavorable).
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Integration rule type criteria |
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Integration rule description criteria |
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
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As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
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As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
|
As indicated above, little weight is given to the species groups, as the proposed classification does not seem to be adequate to define the species in the Spanish sea basin districts. It is also not considered appropriate for integration at the level of all seabirds, as evaluation elements deserve specific attention, whether or not they are considered to be the whole bird community in BEB.
As regards the integration of the different criteria in order to provide a joint assessment of BBE by species, the ICES recommendations have been followed (ICES 2018 (a)), with the amendments recently incorporated by the JWGBIRD (ICES 2018b). In a nutshell, any species that do not comply with the BBE for a primary criterion would be considered not to comply with the BEA at the level of the Demarcación Marina. In this regard, criterion D1C3 on C1D2 has been given priority in this case, for the reasons set out above.
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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 |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Description overall status |
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Assessments period |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
2012-2018 |
Related pressures |
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Related targets |
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