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Table 2.<br />

Latest Saker falcon<br />

population estimates<br />

<strong>in</strong> Europe, <strong>in</strong>dicat<strong>in</strong>g<br />

those countries that<br />

hold at least 1% of the<br />

European population.<br />

Country No. of breed<strong>in</strong>g pairs Year %<br />

Austria 25–30 2010 [17] 4<br />

Bulgaria 0–8 2012 [18]<br />

Croatia 3–5 2010 [19] 1<br />

Czech Republic 20–25 2013 [20] 3<br />

Germany 0–1 2006 [9]<br />

[21]<br />

Hungary 241–245 2012 33<br />

FYRO Macedonia 0–3 2013 [22]<br />

Moldova 10–12 2010 [19] 2<br />

was on the br<strong>in</strong>k of ext<strong>in</strong>ction <strong>in</strong> the 1970s [35] . In<br />

Ukra<strong>in</strong>e, which also holds 45% of the Saker falcon<br />

population <strong>in</strong> Europe, the population suffered<br />

significant decl<strong>in</strong>es s<strong>in</strong>ce the 1950/60s, but is now<br />

considered to be relatively stable [10, 28, 36] . In Bulgaria,<br />

Saker falcons used to be common and widespread<br />

before the 1930s [37] , but are now close to ext<strong>in</strong>ction<br />

(Table 2), and the last documented successful<br />

breed<strong>in</strong>g attempt was <strong>in</strong> 1997 [38] .<br />

Table 3.<br />

Major threats that<br />

drove Saker falcon<br />

decl<strong>in</strong>e and may<br />

still constra<strong>in</strong> the<br />

population [9] .<br />

Threat Description Impact<br />

Agricultural<br />

<strong>in</strong>tensification<br />

Agricultural<br />

abandonment<br />

Wood and pulp<br />

plantations<br />

Conversion of grasslands <strong>in</strong>to arable land, or <strong>in</strong>to v<strong>in</strong>eyards<br />

<strong>in</strong> Bulgaria, leads to a reduction <strong>in</strong> prey availability.<br />

Disturbance at nest sites from agricultural operations.<br />

Poison<strong>in</strong>g by pesticides or other chemicals, result<strong>in</strong>g <strong>in</strong><br />

low productivity.<br />

Tree fell<strong>in</strong>g <strong>in</strong> steppe and pseudo-steppe may limit<br />

nest availability.<br />

Decrease <strong>in</strong> graz<strong>in</strong>g animal stock results <strong>in</strong> lower prey<br />

availability.<br />

Loss of forag<strong>in</strong>g habitat through afforestation of<br />

agricultural land.<br />

Disturbance at nest sites from forestry activities.<br />

High<br />

locally<br />

Medium<br />

Unknown<br />

Local<br />

High<br />

Local<br />

Other Nest collapse when old or weak nests are occupied. High<br />

Hunt<strong>in</strong>g and<br />

collect<strong>in</strong>g<br />

Persecution/<br />

control<br />

Un<strong>in</strong>tentional<br />

effects of hunt<strong>in</strong>g<br />

and collect<strong>in</strong>g<br />

Transportation and<br />

service corridors<br />

Trapp<strong>in</strong>g for use <strong>in</strong> falconry, especially <strong>in</strong> the Middle<br />

East, Pakistan and North Africa.<br />

Nest robb<strong>in</strong>g was critical <strong>in</strong> the Czech Republic,<br />

Slovakia and possibly Bulgaria, Ukra<strong>in</strong>e and Russia.<br />

Illegal shoot<strong>in</strong>g, especially <strong>in</strong> the migratory Asian<br />

populations.<br />

Destruction of artificial nests where considered a<br />

threat by game keepers, particularly <strong>in</strong> the Czech<br />

Republic.<br />

Persecution by pigeon-fanciers (poison<strong>in</strong>g, shoot<strong>in</strong>g,<br />

destruction of nest) <strong>in</strong> Serbia, Hungary, Slovakia<br />

Suslik eradication – considered a pest or competitor<br />

with livestock.<br />

Un<strong>in</strong>tentional poison<strong>in</strong>g from bait <strong>in</strong>tended for foxes<br />

and other verm<strong>in</strong>.<br />

Electrocution by power l<strong>in</strong>es.<br />

Renewable energy Collisions with w<strong>in</strong>d turb<strong>in</strong>es. Low<br />

Residential and<br />

commercial<br />

development<br />

M<strong>in</strong><strong>in</strong>g and<br />

quarry<strong>in</strong>g<br />

Invasive nonnative/alien<br />

species<br />

Problematic native<br />

species<br />

Climate change and<br />

severe weather<br />

Poland 0–2 2007 [23]<br />

Romania 10 2010 [8] 1<br />

Serbia 25–35 2013 [24] 4<br />

Slovakia 40–45 2012 [25] 6<br />

[19]<br />

Ukra<strong>in</strong>e 315–345 2010 45<br />

W<strong>in</strong>d farm development has resulted <strong>in</strong> loss of<br />

breed<strong>in</strong>g and forag<strong>in</strong>g areas <strong>in</strong> east Austria, west<br />

Hungary, north Serbia, west and southeast Romania<br />

Infrastructure development results <strong>in</strong> loss of Suslik<br />

colonies.<br />

Quarry<strong>in</strong>g <strong>in</strong> some parts of the species’ range results<br />

<strong>in</strong> loss of nest-sites.<br />

Hybridisation with escaped hybrid falcons.<br />

Nest predation by natural predators.<br />

Extreme weather can cause nest collapse or death of<br />

eggs or small chicks.<br />

Low<br />

Potentially<br />

high<br />

Potentially<br />

high locally<br />

Medium<br />

Local<br />

Low<br />

Low<br />

High<br />

High<br />

Medium<br />

to locally<br />

high<br />

Medium<br />

Local<br />

Unknown<br />

Low<br />

Low<br />

Distribution:<br />

current status and changes<br />

S<strong>in</strong>ce the mid-1900s, Saker falcon distribution<br />

has become fragmented as a result of population<br />

decl<strong>in</strong>es and range contractions, especially <strong>in</strong><br />

southeast Europe [5, 9] , and the species became<br />

ext<strong>in</strong>ct from the European part of Russia <strong>in</strong> the early<br />

21 st century. In the late 20 th century, populations<br />

have undergone shifts with<strong>in</strong> their regional distribution,<br />

as a result of chang<strong>in</strong>g habitat occupancy [38] .<br />

In central Europe, follow<strong>in</strong>g the abandonment of<br />

graz<strong>in</strong>g <strong>in</strong> the foothills and mounta<strong>in</strong>s after 1990<br />

and the end of the communist regime, Saker falcon<br />

territories <strong>in</strong> mounta<strong>in</strong>s and hills were abandoned<br />

<strong>in</strong> favour of lowland agricultural areas, where the<br />

species cont<strong>in</strong>ues to expand, occupy<strong>in</strong>g new (but<br />

probably historically used) areas [8, 30] . Similarly, <strong>in</strong><br />

eastern Europe, Saker falcons decl<strong>in</strong>ed <strong>in</strong> the forest<br />

steppe, but rema<strong>in</strong>ed and possibly <strong>in</strong>creased <strong>in</strong><br />

the southern steppe zone [28, 33, 38] . Most nest sites for<br />

the species <strong>in</strong> central and eastern Europe are now<br />

electricity pylons [38] and artificial nests are used<br />

extensively by Saker falcons <strong>in</strong> the Carpathian<br />

Bas<strong>in</strong> [8, 30, 35] .<br />

Major threats<br />

The Saker falcon suffered decl<strong>in</strong>es <strong>in</strong> central and<br />

eastern Europe <strong>in</strong> the 19 th and 20 th centuries [9, 38] .<br />

The ma<strong>in</strong> reasons <strong>in</strong>clude persecution, and habitat<br />

loss and degradation, due to decl<strong>in</strong>es <strong>in</strong> key prey<br />

species, as a result of abandonment of pastoralism<br />

after the end of the communist regime,<br />

while ongo<strong>in</strong>g nest robb<strong>in</strong>g for falconry had<br />

important negative effects on already decl<strong>in</strong><strong>in</strong>g<br />

populations [8, 9, 27, 38] . Agricultural <strong>in</strong>tensification<br />

has also had negative impacts on Saker falcons,<br />

result<strong>in</strong>g <strong>in</strong> habitat loss for the species’ prey<br />

(Suslik) [8, 9, 30, 38] . However, it is important to note that<br />

<strong>in</strong>tensive agricultural areas currently hold some of<br />

the highest Saker falcon breed<strong>in</strong>g pair densities <strong>in</strong><br />

Hungary [8] , <strong>in</strong>dicat<strong>in</strong>g that the species can utilise<br />

such habitats given adequate prey and (artificial)<br />

nest site availability.<br />

206

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