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
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
Related targets
  • A.E.1
  • A.E.10
  • A.E.2.
  • A.E.3
  • A.E.5
  • A.E.6
  • A.E.7
  • A.E.8
  • B.E.16
  • B.E.17
  • C.E.15
  • C.E.16
  • C.E.17
  • C.E.18
  • C.E.3
  • C.E.4
  • C.E.6
  • C.E.7
  • C.E.8
  • A.E.1
  • A.E.10
  • A.E.2.
  • A.E.3
  • A.E.5
  • A.E.6
  • A.E.7
  • A.E.8
  • B.E.16
  • B.E.17
  • C.E.15
  • C.E.16
  • C.E.17
  • C.E.18
  • C.E.3
  • C.E.4
  • C.E.6
  • C.E.7
  • C.E.8
  • A.E.1
  • A.E.10
  • A.E.2.
  • A.E.3
  • A.E.5
  • A.E.6
  • A.E.7
  • A.E.8
  • B.E.16
  • B.E.17
  • C.E.15
  • C.E.16
  • C.E.17
  • C.E.18
  • C.E.3
  • C.E.4
  • C.E.6
  • C.E.7
  • C.E.8
  • A.E.1
  • A.E.10
  • A.E.2.
  • A.E.3
  • A.E.5
  • A.E.6
  • A.E.7
  • A.E.8
  • B.E.16
  • B.E.17
  • C.E.15
  • C.E.16
  • C.E.17
  • C.E.18
  • C.E.3
  • C.E.4
  • C.E.6
  • C.E.7
  • C.E.8
  • A.E.1
  • A.E.10
  • A.E.2.
  • A.E.3
  • A.E.5
  • A.E.6
  • A.E.7
  • A.E.8
  • B.E.16
  • B.E.17
  • C.E.15
  • C.E.16
  • C.E.17
  • C.E.18
  • C.E.3
  • C.E.4
  • C.E.6
  • C.E.7
  • C.E.8
  • A.E.1
  • A.E.10
  • A.E.2
  • A.E.3
  • A.E.5
  • A.E.6
  • A.E.7
  • A.E.8
  • B.E.16
  • B.E.17
  • C.E.15
  • C.E.16
  • C.E.17
  • C.E.18
  • C.E.3
  • C.E.4
  • C.E.6
  • C.E.7
  • C.E.8
  • A.E.1
  • A.E.10
  • A.E.2
  • A.E.3
  • A.E.5
  • A.E.6
  • A.E.7
  • A.E.8
  • B.E.16
  • B.E.17
  • C.E.15
  • C.E.16
  • C.E.17
  • C.E.18
  • C.E.3
  • C.E.4
  • C.E.6
  • C.E.7
  • C.E.8
  • A.E.1
  • A.E.10
  • A.E.2
  • A.E.3
  • A.E.5
  • A.E.6
  • A.E.7
  • A.E.8
  • B.E.16
  • B.E.17
  • C.E.15
  • C.E.16
  • C.E.17
  • C.E.18
  • C.E.3
  • C.E.4
  • C.E.6
  • C.E.7
  • C.E.8
  • A.E.1
  • A.E.10
  • A.E.2
  • A.E.3
  • A.E.5
  • A.E.6
  • A.E.7
  • A.E.8
  • B.E.16
  • B.E.17
  • C.E.15
  • C.E.16
  • C.E.17
  • C.E.18
  • C.E.3
  • C.E.4
  • C.E.6
  • C.E.7
  • C.E.8
  • A.E.1
  • A.E.10
  • A.E.2
  • A.E.3
  • A.E.5
  • A.E.6
  • A.E.7
  • A.E.8
  • B.E.16
  • B.E.17
  • C.E.15
  • C.E.16
  • C.E.17
  • C.E.18
  • C.E.3
  • C.E.4
  • C.E.6
  • C.E.7
  • C.E.8
  • A.E.1
  • A.E.10
  • A.E.2
  • A.E.3
  • A.E.5
  • A.E.6
  • A.E.7
  • A.E.8
  • B.E.16
  • B.E.17
  • C.E.15
  • C.E.16
  • C.E.17
  • C.E.18
  • C.E.3
  • C.E.4
  • C.E.6
  • C.E.7
  • C.E.8
  • A.E.1
  • A.E.10
  • A.E.2
  • A.E.3
  • A.E.5
  • A.E.6
  • A.E.7
  • A.E.8
  • B.E.16
  • B.E.17
  • C.E.15
  • C.E.16
  • C.E.17
  • C.E.18
  • C.E.3
  • C.E.4
  • C.E.6
  • C.E.7
  • C.E.8
  • A.E.1
  • A.E.10
  • A.E.2
  • A.E.3
  • A.E.5
  • A.E.6
  • A.E.7
  • A.E.8
  • B.E.16
  • B.E.17
  • C.E.15
  • C.E.16
  • C.E.17
  • C.E.18
  • C.E.3
  • C.E.4
  • C.E.6
  • C.E.7
  • C.E.8
  • A.E.1
  • A.E.10
  • A.E.2
  • A.E.3
  • A.E.5
  • A.E.6
  • A.E.7
  • A.E.8
  • B.E.16
  • B.E.17
  • C.E.15
  • C.E.16
  • C.E.17
  • C.E.18
  • C.E.3
  • C.E.4
  • C.E.6
  • C.E.7
  • C.E.8
  • A.E.1
  • A.E.10
  • A.E.2
  • A.E.3
  • A.E.5
  • A.E.6
  • A.E.7
  • A.E.8
  • B.E.16
  • B.E.17
  • C.E.15
  • C.E.16
  • C.E.17
  • C.E.18
  • C.E.3
  • C.E.4
  • C.E.6
  • C.E.7
  • C.E.8
  • A.E.1
  • A.E.10
  • A.E.2
  • A.E.3
  • A.E.5
  • A.E.6
  • A.E.7
  • A.E.8
  • B.E.16
  • B.E.17
  • C.E.15
  • C.E.16
  • C.E.17
  • C.E.18
  • C.E.3
  • C.E.4
  • C.E.6
  • C.E.7
  • C.E.8
  • A.E.1
  • A.E.10
  • A.E.2
  • A.E.3
  • A.E.5
  • A.E.6
  • A.E.7
  • A.E.8
  • B.E.16
  • B.E.17
  • C.E.15
  • C.E.16
  • C.E.17
  • C.E.18
  • C.E.3
  • C.E.4
  • C.E.6
  • C.E.7
  • C.E.8
  • A.E.1
  • A.E.10
  • A.E.2
  • A.E.3
  • A.E.5
  • A.E.6
  • A.E.7
  • A.E.8
  • B.E.16
  • B.E.17
  • C.E.15
  • C.E.16
  • C.E.17
  • C.E.18
  • C.E.3
  • C.E.4
  • C.E.6
  • C.E.7
  • C.E.8
  • A.E.1
  • A.E.10
  • A.E.2
  • A.E.3
  • A.E.5
  • A.E.6
  • A.E.7
  • A.E.8
  • B.E.16
  • B.E.17
  • C.E.15
  • C.E.16
  • C.E.17
  • C.E.18
  • C.E.3
  • C.E.4
  • C.E.6
  • C.E.7
  • C.E.8
  • A.E.1
  • A.E.10
  • A.E.2
  • A.E.3
  • A.E.5
  • A.E.6
  • A.E.7
  • A.E.8
  • B.E.16
  • B.E.17
  • C.E.15
  • C.E.16
  • C.E.17
  • C.E.18
  • C.E.3
  • C.E.4
  • C.E.6
  • C.E.7
  • C.E.8
  • A.E.1
  • A.E.10
  • A.E.2
  • A.E.3
  • A.E.5
  • A.E.6
  • A.E.7
  • A.E.8
  • B.E.16
  • B.E.17
  • C.E.15
  • C.E.16
  • C.E.17
  • C.E.18
  • C.E.3
  • C.E.4
  • C.E.6
  • C.E.7
  • C.E.8
  • A.E.1
  • A.E.10
  • A.E.2
  • A.E.3
  • A.E.5
  • A.E.6
  • A.E.7
  • A.E.8
  • B.E.16
  • B.E.17
  • C.E.15
  • C.E.16
  • C.E.17
  • C.E.18
  • C.E.3
  • C.E.4
  • C.E.6
  • C.E.7
  • C.E.8
  • A.E.1
  • A.E.10
  • A.E.2
  • A.E.3
  • A.E.5
  • A.E.6
  • A.E.7
  • A.E.8
  • B.E.16
  • B.E.17
  • C.E.15
  • C.E.16
  • C.E.17
  • C.E.18
  • C.E.3
  • C.E.4
  • C.E.6
  • C.E.7
  • C.E.8

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
  • SB_SBU_BP
  • SB_SBU_BP
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).
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.
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
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
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
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
  • Disturbance of species (e.g. where they breed, rest and feed) due to human presence
  • Input or spread of non-indigenous species
Related targets
  • A.L.1
  • A.L.10
  • A.L.2
  • A.L.3
  • A.L.5
  • A.L.6
  • A.L.7
  • A.L.8
  • B.L.16
  • B.L.17
  • C.L.15
  • C.L.16
  • C.L.17
  • C.L.18
  • C.L.3
  • C.L.4
  • C.L.5
  • C.L.6
  • C.L.7
  • C.L.8
  • A.L.1
  • A.L.10
  • A.L.2
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