130925-studie-wildlife-comeback-in-europe
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Country No. of breed<strong>in</strong>g pairs Trend Year %<br />
Austria 12–19 Stable 2008<br />
Belarus 1–5 Stable [14] 2008<br />
Belgium 150 + 2008 1<br />
Bulgaria 0–1 ? 2008<br />
Czech Republic 100–120 + 2007<br />
Denmark 75–80 + 2008<br />
France 2,656 Stable 2009 [15] 11<br />
Germany 10,100–12,300 Stable 2009 [16] 47<br />
Hungary 5–10 Stable 2010 [17]<br />
Republic of Ireland 25–35 + [18] 2013 [18]<br />
Italy 314–426 + 2008 2<br />
Latvia 1 + 2010 [19]<br />
Liechtenste<strong>in</strong> 0–1 ? 2008<br />
Lithuania 10–20 + 2013 [20]<br />
Luxembourg 40 Stable 2009 [21]<br />
Netherlands 1 ? 2012 [22]<br />
Poland 1,000–1,500 + [14] 2009 [23] 5<br />
Portugal 36–67 - [14] 2001<br />
Russia 5–10 ? 2003<br />
Serbia 4–6 ? 2008 [24]<br />
Slovakia 10–15 - 2012 [25]<br />
Spa<strong>in</strong> 2,000–2,200 - [14] 2005 9<br />
Sweden 1,933–2,181 + 2012 [26] 9<br />
Switzerland 1,200–1,500 + 2009 [27] 6<br />
UK 2,200 + 2013 [28] 9<br />
Table 2. Latest Red kite population estimates <strong>in</strong> Europe, <strong>in</strong>dicat<strong>in</strong>g those<br />
countries with more than 1% of the total population. Unless otherwise stated,<br />
data are from Aebischer (2009) [4] .<br />
Table 3. Major threats that drove Red kite decl<strong>in</strong>e and may still constra<strong>in</strong> the<br />
population [14] .<br />
Threat Description Impact<br />
Un<strong>in</strong>tentional Poison<strong>in</strong>g from illegal baits.<br />
Critical<br />
effects of hunt<strong>in</strong>g<br />
and collect<strong>in</strong>g Secondary poison<strong>in</strong>g from consumption of<br />
rodents poisoned with rodenticides <strong>in</strong> managed<br />
High<br />
grasslands.<br />
Hunt<strong>in</strong>g and<br />
collect<strong>in</strong>g<br />
Agricultural<br />
<strong>in</strong>tensification<br />
Livestock farm<strong>in</strong>g<br />
and ranch<strong>in</strong>g<br />
Renewable<br />
energy<br />
Transportation<br />
and service<br />
corridors<br />
Wood and pulp<br />
plantations<br />
Secondary lead poison<strong>in</strong>g.<br />
Illegal shoot<strong>in</strong>g and trapp<strong>in</strong>g.<br />
Habitat degradation and loss due to agricultural<br />
<strong>in</strong>tensification, especially plough<strong>in</strong>g of permanent<br />
grasslands and homogenisation of the farmed<br />
landscape. Loss of non-farmed elements, e.g.<br />
hedgerows, trees, uncultivated field edges, results<br />
<strong>in</strong> loss of nest<strong>in</strong>g and feed<strong>in</strong>g sites.<br />
Farm<strong>in</strong>g activities also cause disturbance of<br />
nest<strong>in</strong>g or roost<strong>in</strong>g sites.<br />
EU sanitary legislation prohibited leav<strong>in</strong>g livestock<br />
carcasses, which resulted <strong>in</strong> a decrease <strong>in</strong> food<br />
availability.<br />
Collision with w<strong>in</strong>d turb<strong>in</strong>es, particularly dur<strong>in</strong>g<br />
the breed<strong>in</strong>g season.<br />
Electrocution on power cables.<br />
Disturbance from forestry operations, particularly<br />
<strong>in</strong> some areas of eastern Europe.<br />
Low<br />
Medium/high<br />
Medium/high<br />
Medium<br />
Medium,<br />
potentially<br />
grow<strong>in</strong>g<br />
Low<br />
Low (local)<br />
Norway and Denmark [2] . More recently, severe<br />
range contractions took place <strong>in</strong> the Baltic States,<br />
the Balkans, central and eastern Europe and southwestern<br />
Russia [2, 31] (Figure 2).<br />
From the 1970s, Red kites began recoloniz<strong>in</strong>g<br />
parts of their range, <strong>in</strong>clud<strong>in</strong>g Denmark and<br />
Belgium [2, 12, 31] , while re<strong>in</strong>troduction projects<br />
resulted <strong>in</strong> the recolonisation of the British Isles [14, 18] .<br />
Major threats<br />
Until the mid-1950s, major decl<strong>in</strong>es <strong>in</strong> Red kite<br />
populations were caused by <strong>in</strong>tensive persecution,<br />
especially dur<strong>in</strong>g 1850–1900 [2, 30–32] . From the 1960s,<br />
habitat degradation due to agricultural <strong>in</strong>tensification,<br />
but also the decl<strong>in</strong>e <strong>in</strong> graz<strong>in</strong>g livestock,<br />
negatively affected Red kites <strong>in</strong> southern and<br />
eastern Europe [14, 30] . In Germany, land-use change<br />
and the <strong>in</strong>tensification of agriculture follow<strong>in</strong>g<br />
reunification of the country <strong>in</strong> 1989 resulted <strong>in</strong><br />
habitat degradation and was the ma<strong>in</strong> cause for<br />
the decl<strong>in</strong>e <strong>in</strong> the German Red kite population <strong>in</strong><br />
the 1990s [4, 33] .<br />
The ma<strong>in</strong> driver for the modern decl<strong>in</strong>e of<br />
the species is mortality through poison<strong>in</strong>g [6, 14] .<br />
As facultative scavengers, Red kites are particularly<br />
sensitive to the illegal use of poison for<br />
control of foxes, wolves, corvids, etc. Recent cases<br />
<strong>in</strong>clude 43% of known causes of mortality <strong>in</strong><br />
France between 2002 and 2007 [34] , 40% <strong>in</strong> Scotland<br />
between 1989 and 2006 [35] , and possibly four birds<br />
<strong>in</strong> Northern Ireland so far <strong>in</strong> 2013 [36] . Red kites are<br />
also highly susceptible to secondary poison<strong>in</strong>g<br />
from consumption of poisoned rodents. Rodenticides<br />
are used to control vole outbreaks <strong>in</strong> agricultural<br />
areas and scavengers feed on the poisoned<br />
carcasses [6, 14] . This is a major threat, particularly <strong>in</strong><br />
Spa<strong>in</strong> and France, where the migratory population<br />
of Red kites w<strong>in</strong>ters [13] .<br />
Mortality of w<strong>in</strong>ter<strong>in</strong>g birds caused by<br />
secondary poison<strong>in</strong>g follow<strong>in</strong>g rodent control<br />
campaigns could partially expla<strong>in</strong> the decl<strong>in</strong>es<br />
suffered by the breed<strong>in</strong>g populations of France and<br />
Germany [6] . It is <strong>in</strong>terest<strong>in</strong>g to note that <strong>in</strong> several<br />
of the populations that are stable or <strong>in</strong>creas<strong>in</strong>g,<br />
such as UK, Sweden, Italy, Czech Republic, and<br />
the region of Auvergne <strong>in</strong> France, many birds are<br />
sedentary, and lack of exposure to poison<strong>in</strong>g <strong>in</strong><br />
the w<strong>in</strong>ter<strong>in</strong>g grounds has been suggested as a<br />
factor beh<strong>in</strong>d the positive trends <strong>in</strong> these populations<br />
[3, 6, 33] .<br />
Other threats <strong>in</strong>clude illegal persecution of<br />
the species, prey decl<strong>in</strong>es and loss of breed<strong>in</strong>g<br />
and forag<strong>in</strong>g habitat due to agricultural <strong>in</strong>tensification,<br />
expansion of w<strong>in</strong>dfarms and electrocution<br />
by power cables [10, 13, 14, 37] .<br />
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