Member State report / Art8 / 2018 / D1-B / North East Atlantic
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 |
Region/subregion | North East Atlantic |
Reported by | Member state |
Member state | Sweden |
Denmark |
Germany |
Netherlands |
Belgium |
France |
United Kingdom |
Ireland |
Spain |
Portugal |
|
---|---|---|---|---|---|---|---|---|---|---|---|
Member state report | |||||||||||
Marine reporting units | MRUs used |
|
|
|
|
|
|
|
|
|
|
Features | Species |
|
|
|
|
|
|
|
|
|
|
Element | Actitis hypoleucos |
|
|||||||||
Element | Alca torda |
|
|
|
|
|
|
|
|||
Element | Anas acuta |
|
|
||||||||
Element | Anas clypeata |
|
|
|
|||||||
Element | Anas crecca |
|
|
||||||||
Element | Anas penelope |
|
|
|
|
||||||
Element | Anas platyrhynchos |
|
|
|
|
|
|||||
Element | Anser albifrons |
|
|
||||||||
Element | Anser anser |
|
|
||||||||
Element | Arenaria interpres |
|
|
|
|
||||||
Element | Aythya ferina |
|
|
|
|||||||
Element | Aythya fuligula |
|
|
|
|||||||
Element | Aythya marila |
|
|
||||||||
Element | Branta bernicla |
|
|
||||||||
Element | Branta canadensis |
|
|
||||||||
Element | Branta leucopsis |
|
|
|
|||||||
Element | Bucephala clangula |
|
|
|
|||||||
Element | Bulweria bulwerii |
|
|||||||||
Element | Calidris alba |
|
|
|
|||||||
Element | Calidris alpina |
|
|
|
|||||||
Element | Calidris canutus |
|
|
|
|||||||
Element | Calidris ferruginea |
|
|||||||||
Element | Calidris maritima |
|
|
|
|||||||
Element | Calonectris borealis |
|
|||||||||
Element | Calonectris diomedea borealis |
|
|
||||||||
Element | Calonectris diomedea diomedea |
|
|||||||||
Element | Cepphus grylle |
|
|
|
|||||||
Element | Charadrius alexandrinus |
|
|
|
|
||||||
Element | Charadrius hiaticula |
|
|
|
|
|
|||||
Element | Chlidonias niger |
|
|||||||||
Element | Clangula hyemalis |
|
|
|
|||||||
Element | Cygnus bewickii |
|
|||||||||
Element | Cygnus columbianus |
|
|||||||||
Element | Cygnus cygnus |
|
|
|
|||||||
Element | Cygnus olor |
|
|
|
|
||||||
Element | Egretta garzetta |
|
|||||||||
Element | Fratercula arctica |
|
|
|
|
|
|||||
Element | Fulica atra |
|
|
|
|||||||
Element | Fulmarus glacialis |
|
|
|
|
||||||
Element | Fulmarus glacialis (Northern fulmar) |
|
|||||||||
Element | Gavia arctica |
|
|
||||||||
Element | Gavia sp. |
|
|||||||||
Element | Gavia stellata |
|
|
|
|||||||
Element | Gelochelidon nilotica |
|
|||||||||
Element | Haematopus ostralegus |
|
|
|
|
|
|||||
Element | Hydrobates castro |
|
|||||||||
Element | Hydrobates monteiroi |
|
|||||||||
Element | Hydrobates pelagicus |
|
|
|
|||||||
Element | Hydrocoloeus minutus |
|
|
|
|||||||
Element | Hydroprogne caspia |
|
|||||||||
Element | Larus argentatus |
|
|
|
|
|
|
||||
Element | Larus audouinii |
|
|||||||||
Element | Larus canus |
|
|
|
|
|
|
||||
Element | Larus fuscus |
|
|
|
|
|
|||||
Element | Larus fuscus graellsii |
|
|||||||||
Element | Larus fuscus intermedius |
|
|||||||||
Element | Larus marinus |
|
|
|
|
|
|
||||
Element | Larus melanocephalus |
|
|
|
|
|
|
||||
Element | Larus michahellis |
|
|
||||||||
Element | Larus ridibundus |
|
|
|
|
|
|||||
Element | Limosa lapponica |
|
|
|
|||||||
Element | Limosa limosa |
|
|
||||||||
Element | Melanitta fusca |
|
|
|
|||||||
Element | Melanitta nigra |
|
|
|
|
|
|||||
Element | Melanitta spp. |
|
|||||||||
Element | Mergellus albellus |
|
|
|
|||||||
Element | Mergus merganser |
|
|
|
|||||||
Element | Mergus serrator |
|
|
|
|
|
|||||
Element | Morus bassanus |
|
|
|
|
|
|||||
Element | Morus bassanus (Northern gannet) |
|
|||||||||
Element | Numenius arquata |
|
|
|
|||||||
Element | Numenius phaeopus |
|
|
||||||||
Element | Oceanodroma castro |
|
|||||||||
Element | Oceanodroma leucorhoa |
|
|||||||||
Element | Pelagic-feeding birds (grouped) |
|
|||||||||
Element | Pelagodroma marina |
|
|||||||||
Element | Phalacrocorax aristotelis |
|
|
|
|
|
|||||
Element | Phalacrocorax carbo |
|
|
|
|
|
|
||||
Element | Philomachus pugnax |
|
|
||||||||
Element | Platalea leucorodia |
|
|
|
|
||||||
Element | Pluvialis apricaria |
|
|
|
|||||||
Element | Pluvialis squatarola |
|
|
|
|||||||
Element | Podiceps auritus |
|
|
||||||||
Element | Podiceps cristatus |
|
|
|
|
||||||
Element | Podiceps grisegena |
|
|||||||||
Element | Pterodroma deserta |
|
|||||||||
Element | Pterodroma madeira |
|
|||||||||
Element | Puffinus gravis |
|
|||||||||
Element | Puffinus griseus |
|
|||||||||
Element | Puffinus lherminieri |
|
|||||||||
Element | Puffinus mauretanicus |
|
|
|
|||||||
Element | Puffinus puffinus |
|
|||||||||
Element | Recurvirostra avosetta |
|
|
|
|
||||||
Element | Rissa tridactyla |
|
|
|
|
|
|
|
|||
Element | Rissa tridactylus (Black-legged kittiwake) |
|
|||||||||
Element | Somateria mollissima |
|
|
|
|
|
|||||
Element | Stercorarius parasiticus |
|
|
|
|
|
|||||
Element | Stercorarius pomarinus |
|
|||||||||
Element | Stercorarius skua |
|
|
|
|
|
|||||
Element | Sterna albifrons |
|
|||||||||
Element | Sterna dougallii |
|
|
|
|
||||||
Element | Sterna hirundo |
|
|
|
|
|
|
|
|
||
Element | Sterna paradisaea |
|
|
|
|
|
|||||
Element | Sterna sandvicensis |
|
|
|
|
|
|
||||
Element | Sternula albifrons |
|
|
|
|
|
|
||||
Element | Tadorna tadorna |
|
|
|
|
|
|||||
Element | Tringa erythropus |
|
|
||||||||
Element | Tringa glareola |
|
|||||||||
Element | Tringa nebularia |
|
|
||||||||
Element | Tringa totanus |
|
|
|
|
||||||
Element | Uria aalge |
|
|
|
|
|
|
|
|
||
Element | Vanellus vanellus |
|
|
|
|||||||
Element2 |
|
|
|||||||||
Element sources | No. of elements per level |
|
|
|
|
|
|
|
|
|
|
Criteria and parameters used (number of parameters) | D1 Birds | ||||||||||
Criteria and parameters used (number of parameters) | D1C1 Mortality rate from incidental by-catch |
|
|
|
|
||||||
Criteria and parameters used (number of parameters) | D1C2 Population abundance (1.2, 1.2.1) |
|
|
|
|
|
|
|
|
|
|
Criteria and parameters used (number of parameters) | D1C3 Population demographic characteristics (1.3, 1.3.1) |
|
|
|
|
|
|
||||
Criteria and parameters used (number of parameters) | D1C4 Population distributional range and pattern (1.1, 1.1.1, 1.1.2, 1.1.3) |
|
|
|
|
|
|
||||
Criteria and parameters used (number of parameters) | D1C5 Habitat for the species |
|
|
||||||||
Threshold values | % of parameters with values (no. of parameters) | 100% (54) |
0% (0) |
27% (66) |
100% (87) |
28% (13) |
35% (50) |
0% (0) |
64% (38) |
22% (21) |
|
Threshold value sources | D1 Birds | ||||||||||
Threshold value sources | D1C1 Mortality rate from incidental by-catch |
|
|
||||||||
Threshold value sources | D1C2 Population abundance (1.2, 1.2.1) |
|
|
|
|
|
|
|
|||
Threshold value sources | D1C3 Population demographic characteristics (1.3, 1.3.1) |
|
|
|
|
|
|
||||
Threshold value sources | D1C4 Population distributional range and pattern (1.1, 1.1.1, 1.1.2, 1.1.3) |
|
|
|
|||||||
Threshold value sources | D1C5 Habitat for the species | ||||||||||
Value achieved upper | % of parameters with values (no. of parameters) | 92% (50) |
62% (80) |
25% (61) |
100% (87) |
28% (13) |
58% (83) |
0% (0) |
40% (24) |
30% (29) |
|
Value achieved lower | % of parameters with values (no. of parameters) | 0% (0) |
61% (79) |
0% (0) |
0% (0) |
28% (13) |
0% (0) |
0% (0) |
0% (0) |
11% (11) |
|
Value unit/Value unit other (count of use per criterion) | D1 Birds | ||||||||||
Value unit/Value unit other (count of use per criterion) | D1C1 Mortality rate from incidental by-catch |
|
|
||||||||
Value unit/Value unit other (count of use per criterion) | D1C2 Population abundance (1.2, 1.2.1) |
|
|
|
|
|
|
|
|
||
Value unit/Value unit other (count of use per criterion) | D1C3 Population demographic characteristics (1.3, 1.3.1) |
|
|
|
|
||||||
Value unit/Value unit other (count of use per criterion) | D1C4 Population distributional range and pattern (1.1, 1.1.1, 1.1.2, 1.1.3) |
|
|
||||||||
Value unit/Value unit other (count of use per criterion) | D1C5 Habitat for the species | ||||||||||
Proportion threshold values | Range of % values (no. of parameters) | Range: 100-100% (87 of 87 parameters) |
Range: 100-100% (108 of 142 parameters) |
Range: 100-100% (2 of 95 parameters) |
|||||||
Proportion values achieved | Range of % values (no. of parameters) | Range: 100-100% (1 of 87 parameters) |
Range: 100-100% (2 of 95 parameters) |
||||||||
Proportion threshold value units | % area of MRU achieving threshold value % area of habitat achieving threshold value |
% of population achieving threshold value |
% of population achieving threshold value |
||||||||
Trends | No. of trends per category |
|
|
|
|
|
|
|
|
|
|
Parameters achieved | No. of parameters per category |
|
|
|
|
|
|
|
|
|
|
Related indicators |
|
|
|
|
|
|
|
|
|
||
Criteria status | No. of criteria per category |
|
|
|
|
|
|
|
|
|
|
Element status | No. of elements per category |
|
|
|
|
|
|
|
|
|
|
Integration rule type for parameters | Not relevant (108 or 100.0%) |
Not relevant (129 or 100.0%) |
OOAO (238 or 100.0%) |
OTH (87 or 100.0%) |
Not relevant (45 or 100.0%) |
Not relevant (85 or 22.1%) OTH (299 or 77.9%) |
Not relevant (64 or 100.0%) |
||||
Integration rule description for parameters |
A method for integrating criteria has not yet been adopted, nor has it been considered possible to integrate the condition in relation to populations of breeding and wintering birds of the same species.
|
No integration
|
For this evaluation, no integration of the parameters filling the D1C2 criterion is carried out. The other criteria are not evaluated, so there is no integration of parameters.
Methods for integrating parameters to assess the status of the D1C2 criterion are not yet defined at European level. The other criteria are not assessed, so there is no integration of parameters. |
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 for criteria | Not relevant (108 or 100.0%) |
Not relevant (129 or 100.0%) |
OOAO (238 or 100.0%) |
OTH (87 or 100.0%) |
Not relevant (45 or 100.0%) |
OTH (384 or 100.0%) |
OTH (12 or 100.0%) |
Not relevant (64 or 100.0%) |
|||
Integration rule description for criteria |
A method for integrating criteria has not yet been adopted, nor has it been considered possible to integrate the condition in relation to populations of breeding and wintering birds of the same species.
|
The criteria were assessed at the level of individual species. A species is in good condition if all criteria meet the relevant thresholds. At the level of the groups of species, the criteria are no longer taken into account.
|
No integration
|
The integration rule is being developed in the framework of the Joint OSPAR/HELCOM/ICES Working Group on Seabirds.
|
Collective expert judgement was used to determine criteria integration. |
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. |
For assessment and integration of environmental status it is essential to collect a wider/diverse set of data, filling gaps for a precision assessment. the suggested integration rule OOAO (WG BEA, 2017) could offer a reliable and robust integration method if the status of each element, criterion, indicator could be assessed with a very high degree of confidence, this is rarely the case.
|
||||
GES extent threshold |
|
|
|
|
|||||||
GES extent achieved |
|
|
|
|
|||||||
GES extent unit |
|
|
|
|
|
||||||
GES achieved | Benthic-feeding birds |
|
|
|
|
|
|
||||
GES achieved | Grazing birds |
|
|
|
|
|
|||||
GES achieved | Pelagic-feeding birds |
|
|
|
|
|
|
|
|
|
|
GES achieved | Surface-feeding birds |
|
|
|
|
|
|
|
|
||
GES achieved | Wading birds |
|
|
|
|
|
|||||
Assessment period | 2011-2016 (108 or 100.0%) |
1999-2011 (129 or 100.0%) |
2012-2018 (238 or 100.0%) |
2012-2015 (87 or 100.0%) |
2011-2016 (13 or 28.9%) 2014 (32 or 71.1%) |
2010-2016 (384 or 100.0%) |
2009-2018 (12 or 100.0%) |
2012-2018 (58 or 47.5%) 2017-2018 (64 or 52.5%) |
2012-2017 (46 or 40.7%) 2012-2018 (42 or 37.2%) 2014-2018 (25 or 22.1%) |
||
Related pressures |
|
|
|
|
|
|
|
|
|||
Related targets | 9 |
5 |
8 |
4 |
5 |
4 |
77 |
15 |