Birds in the European Union - BirdLife International
Birds in the European Union - BirdLife International
Birds in the European Union - BirdLife International
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12<br />
■ The population trends of Annex I species <strong>in</strong> <strong>the</strong><br />
EU15 versus Annex I species <strong>in</strong> <strong>the</strong> countries<br />
outside <strong>the</strong> EU15<br />
In order to <strong>in</strong>vestigate fur<strong>the</strong>r <strong>the</strong> effect of <strong>in</strong>clusion on Annex<br />
I of <strong>the</strong> <strong>Birds</strong> Directive, we compared <strong>the</strong> population trends of<br />
Annex I species <strong>in</strong> <strong>the</strong> EU15 countries with <strong>the</strong> trend for <strong>the</strong><br />
same species <strong>in</strong> countries outside <strong>the</strong> EU15.<br />
The results aga<strong>in</strong> showed positive trends for <strong>the</strong> EU15 and<br />
a significant difference between EU15 and countries outside<br />
<strong>the</strong> EU15.<br />
Conclusion:<br />
Annex I species <strong>in</strong> <strong>the</strong> EU15 did better than <strong>the</strong><br />
same species <strong>in</strong> non-EU15 countries as shown by<br />
population trends <strong>in</strong> <strong>the</strong> period between 1990–2000.<br />
■ Action plans for Europe’s most threatened birds:<br />
help<strong>in</strong>g stop decl<strong>in</strong>es<br />
In July 2004, <strong>BirdLife</strong> <strong>International</strong> produced a report for <strong>the</strong><br />
<strong>European</strong> Commission review<strong>in</strong>g implementation of <strong>the</strong> first<br />
23 <strong>in</strong>ternational Species Action Plans (SAPs), as adopted <strong>in</strong><br />
1996 (Nagy and Crockford 2004). <strong>BirdLife</strong> <strong>International</strong> found<br />
out <strong>the</strong> follow<strong>in</strong>g:<br />
Implementation of <strong>the</strong> SAPs was fullest <strong>in</strong> <strong>the</strong> UK, <strong>the</strong><br />
Ne<strong>the</strong>rlands, Hungary, Portugal and Austria.<br />
The most complete implementation was for two critically<br />
endangered birds, Z<strong>in</strong>o’s Petrel Pterodroma madeira and<br />
Slender-billed Curlew Numenius tenuirostris, with Dalmatian<br />
Pelican Pelecanus crispus be<strong>in</strong>g <strong>the</strong> next most complete.<br />
Significant progress was made <strong>in</strong> implementation of 18 of<br />
<strong>the</strong> 23 species action plans.<br />
Progress was limited for only two species; White-headed<br />
Duck Oxyura leucocephala, due to <strong>in</strong>adequate eradication<br />
of <strong>the</strong> <strong>in</strong>troduced Ruddy Duck Oxyura jamaicensis and<br />
Lesser Kestrel Falco naumanni.<br />
The EU LIFE Nature 2 fund contributed to <strong>the</strong> conservation<br />
of all 23 species; it was <strong>the</strong> ma<strong>in</strong> driv<strong>in</strong>g force <strong>in</strong> <strong>the</strong><br />
conservation of <strong>the</strong> eight island endemics <strong>in</strong> Portugal and<br />
Spa<strong>in</strong>, and has played a very significant role <strong>in</strong> <strong>the</strong><br />
implementation of some 14 plans <strong>in</strong> Spa<strong>in</strong> and Greece.<br />
Overall, <strong>BirdLife</strong> <strong>International</strong> found that <strong>the</strong> situation has<br />
improved for 12 species, been ma<strong>in</strong>ta<strong>in</strong>ed for three and decl<strong>in</strong>ed<br />
for six species. Data were <strong>in</strong>sufficient to assess <strong>the</strong> status change<br />
of two Canarian endemics (Nagy and Crockford, 2004).<br />
Conclusion:<br />
Significant progress has been made for certa<strong>in</strong><br />
species through <strong>the</strong> implementation of Species<br />
Action Plans.<br />
■ The population trends of Annex I species with an<br />
<strong>in</strong>ternational Species Action Plan compared to<br />
those without a SAP <strong>in</strong> <strong>the</strong> EU 15<br />
In order to <strong>in</strong>vestigate fur<strong>the</strong>r whe<strong>the</strong>r hav<strong>in</strong>g a Species Action<br />
Plan (SAP) can make a difference for <strong>the</strong> Conservation Status<br />
of a species, <strong>the</strong> population trends of those Annex I species with<br />
a SAP were compared with those without a SAP. The comparison<br />
was done on 166 Annex I species tak<strong>in</strong>g <strong>in</strong>to account those 23<br />
with a SAP from <strong>the</strong> mid-1990s. The results showed that <strong>the</strong><br />
species with a SAP did better compared to those without.<br />
<strong>Birds</strong> <strong>in</strong> <strong>the</strong> <strong>European</strong> <strong>Union</strong>: a status assessment – Results<br />
Conclusion:<br />
Annex I species with a Species Action Plan did<br />
better than those without a SAP <strong>in</strong> <strong>the</strong> EU15, <strong>in</strong><br />
<strong>the</strong> period 1990–2000.<br />
■ IBAs and SPAs for species with a Species Action<br />
Plan (SAP)<br />
Accord<strong>in</strong>g to <strong>the</strong> same report (Nagy and Crockford, 2004) it<br />
was concluded that overall <strong>the</strong> obligations aris<strong>in</strong>g from article<br />
4 of <strong>the</strong> Directive had played an important role <strong>in</strong> <strong>the</strong> protection<br />
of species with a SAP. In most cases, <strong>the</strong> Important Bird Areas<br />
(IBA) that had been proposed for those species had been<br />
classified as SPAs, and <strong>the</strong>reby covered <strong>the</strong> majority of <strong>the</strong><br />
populations. The species for which this was not <strong>the</strong> case were:<br />
Imperial Eagle Aquila heliaca, Lesser Kestrel Falco naumanni,<br />
Corncrake Crex crex, Great Bustard Otis tarda, Houbara<br />
Bustard Chlamydotis undulata and Aquatic Warbler<br />
Acrocephalus paludicola.<br />
The low coverage of species like Corncrake and Aquatic<br />
Warbler results from <strong>the</strong> fact that <strong>the</strong> large part of <strong>the</strong><br />
population of <strong>the</strong>se species occur <strong>in</strong> <strong>the</strong> new Member States<br />
and at <strong>the</strong> time of compil<strong>in</strong>g <strong>the</strong> report above <strong>the</strong>se countries<br />
had not submitted SPA lists yet.<br />
The almost complete coverage of <strong>the</strong>se species by <strong>the</strong> SPA<br />
network can be one of <strong>the</strong> reasons why <strong>the</strong>se species do better<br />
when compared to o<strong>the</strong>r Annex I species.<br />
Conclusion:<br />
The almost complete coverage of <strong>the</strong> species with<br />
SAPs by <strong>the</strong> SPA network can be one of <strong>the</strong> reasons<br />
why <strong>the</strong>se species do better <strong>in</strong> general when<br />
compared to o<strong>the</strong>r Annex I species.<br />
■ The population trends of bird species with<br />
differ<strong>in</strong>g migration strategies<br />
<strong>BirdLife</strong> <strong>International</strong> also compared <strong>the</strong> population trends of<br />
species with differ<strong>in</strong>g migration strategies. These were species<br />
that are long-distance migrants, i.e. cross <strong>the</strong> Sahara to get to<br />
<strong>the</strong>ir w<strong>in</strong>ter<strong>in</strong>g grounds, short distance migrants and partial<br />
migrants or residents. Short-distance migrants are species which<br />
w<strong>in</strong>ter <strong>in</strong> Europe, North Africa or <strong>the</strong> Middle East, while partial<br />
migrants or residents, are species, which do not migrate or<br />
migrate very short distances often respond<strong>in</strong>g to adverse<br />
wea<strong>the</strong>r conditions. The results show that long distance<br />
migrants are do<strong>in</strong>g significantly worse than residents or shortdistance<br />
migrants. The overall trend for long distance migrants<br />
was one of strong decl<strong>in</strong>e at EU and Pan-<strong>European</strong> level. This<br />
was significantly different to <strong>the</strong> trends of short-distance<br />
migrants and residents.<br />
Conclusion:<br />
Long-distance migrants are decl<strong>in</strong><strong>in</strong>g alarm<strong>in</strong>gly.<br />
2. LIFE Nature, <strong>the</strong> EU F<strong>in</strong>ancial Instrument, <strong>in</strong>troduced <strong>in</strong> 1992 co-f<strong>in</strong>ances projects aimed at conservation of natural habitats and <strong>the</strong> wild fauna and flora of EU <strong>in</strong>terest, <strong>in</strong> support of<br />
implementation of <strong>the</strong> <strong>Birds</strong> and Habitats Directives.