130925-studie-wildlife-comeback-in-europe
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tunity for recovery, but with on-go<strong>in</strong>g exploitation<br />
populations cont<strong>in</strong>ued to decl<strong>in</strong>e [23] . Although the<br />
species has not been formally protected s<strong>in</strong>ce the<br />
Second World War, changes <strong>in</strong> hunt<strong>in</strong>g practices<br />
and forestry have allowed the species to become<br />
widespread and numerous [23] .<br />
Abundance and distribution: changes<br />
% change<br />
400<br />
300<br />
200<br />
100<br />
0<br />
In 1810, the Eurasian elk was distributed across an<br />
area of around 160,000 km 2 <strong>in</strong> a number of isolated<br />
populations. These ranged across south-central<br />
Sweden and Norway, F<strong>in</strong>nish and Russian Karelia,<br />
southeastern Murmansk, and some of European<br />
Russia. One cont<strong>in</strong>uous population ranged from<br />
Arkhangelsk to the Urals, another large population<br />
reached from the Moscow region <strong>in</strong>to Belarus, and<br />
there were also five smaller satellite populations<br />
(Figure 1a). By 1955, the species’ range had <strong>in</strong>creased<br />
by around 150%, connect<strong>in</strong>g formerly isolated areas<br />
(Figure 1a). Cont<strong>in</strong>ued expansion resulted <strong>in</strong> an<br />
occupied area that was estimated to be 280% larger<br />
than the 1810 distribution <strong>in</strong> 2008 (Figures 1a and b).<br />
With significant spread <strong>in</strong>to central Europe, the elk’s<br />
current distribution encompasses Scand<strong>in</strong>avia,<br />
most of northern and central European Russia<br />
and two-thirds of Poland. It is also reach<strong>in</strong>g <strong>in</strong>to<br />
Germany, northern Austria, the southern Czech<br />
Republic, northern and western Belarus and northwestern<br />
Ukra<strong>in</strong>e (Figures 1a and B), as well as the<br />
northern Caucasus lowlands [11] . However, there have<br />
also been contractions <strong>in</strong> range <strong>in</strong> southern Belarus,<br />
Ukra<strong>in</strong>e and Denmark (Figures 1a and b).<br />
This overall positive trend <strong>in</strong> distribution is <strong>in</strong><br />
l<strong>in</strong>e with change <strong>in</strong> population size. Monitored<br />
populations of the Eurasian elk <strong>in</strong> Europe appear<br />
to have <strong>in</strong>creased <strong>in</strong> abundance by around 220%<br />
between 1964 and 2005 (Figure 2), although there<br />
is large regional variation underly<strong>in</strong>g this average.<br />
The greatest recovery occurred <strong>in</strong> the 1960s, as has<br />
been reported <strong>in</strong> the literature [24] , with population<br />
size <strong>in</strong>creas<strong>in</strong>g by 210%. The rate of growth then<br />
slowed, with a 25% <strong>in</strong>crease <strong>in</strong> the 1970s, and<br />
stability or slight decl<strong>in</strong>e thereafter (Figure 2). It<br />
should be noted, however, that this overall trend<br />
may be mask<strong>in</strong>g differences at the regional level, as<br />
numbers have <strong>in</strong>creased markedly <strong>in</strong> Scand<strong>in</strong>avia<br />
<strong>in</strong> recent decades [11] . The overall trend reported<br />
here is based on 18 populations from the species’<br />
current range, cover<strong>in</strong>g a m<strong>in</strong>imum of 322,000<br />
<strong>in</strong>dividuals. This therefore represents 45% of<br />
the total estimated European population from<br />
2004–7, cover<strong>in</strong>g around 75% of the species’ range<br />
countries. Population abundance data are miss<strong>in</strong>g<br />
from the western edge of the elk’s range, namely<br />
western Poland, the Czech Republic and Germany.<br />
-100<br />
Drivers of recovery<br />
1960s 1970s 1980s 1990s 2000–05 1964–2005<br />
A review of the literature suggests that while<br />
overall trends are positive, the European elk<br />
experienced three phases of decl<strong>in</strong>e <strong>in</strong> eastern<br />
Europe from which this resurgence has taken<br />
place [26] . The fragmented distribution of the species<br />
<strong>in</strong> the early 1800s (Figure 1a) was likely the result<br />
of the first phase of decl<strong>in</strong>e between 1800 and<br />
1850 [26] , which was marked by gradual change, local<br />
extirpation and range contraction followed by<br />
swift recovery [26] . The second phase <strong>in</strong> the 1920s,<br />
attributed to over-exploitation result<strong>in</strong>g from<br />
economic hardship and fam<strong>in</strong>e, led to smaller<br />
range decreases than previously, but recovery<br />
was delayed for unknown reasons [26] . Populations<br />
recovered with the reoccupation of the forest<br />
zone, although this process was slow due to the<br />
destruction of a formerly healthy population<br />
structure [26] . Our analysis showed a slight decrease<br />
from 1990 (Figure 2), which matches the third<br />
phase of decl<strong>in</strong>e normally attributed to political<br />
<strong>in</strong>stability lead<strong>in</strong>g to <strong>in</strong>appropriate management<br />
decisions [26] .<br />
The variability <strong>in</strong> population change <strong>in</strong> the data<br />
set means that clear reasons for <strong>wildlife</strong> <strong>comeback</strong><br />
are difficult to discern, but there are common<br />
themes (Table 3). Regional-level trends show that<br />
populations <strong>in</strong> eastern Europe have decl<strong>in</strong>ed, while<br />
northern European elk (e.g. from F<strong>in</strong>land, Norway,<br />
Poland, and Sweden) have fared better. In addition,<br />
populations from boreal forest and taiga biomes<br />
showed <strong>in</strong>creases <strong>in</strong> abundance, while temperate<br />
broad-leafed forest and temperate grasslands<br />
have decreased. Management was found to have<br />
a positive effect on European elk abundance <strong>in</strong> a<br />
range of locations, which <strong>in</strong>cluded the adoption<br />
of new hunt<strong>in</strong>g pr<strong>in</strong>ciples <strong>in</strong> Russia and F<strong>in</strong>land,<br />
reforestation <strong>in</strong> F<strong>in</strong>land, and legal protection <strong>in</strong><br />
Poland.<br />
Historically, decl<strong>in</strong>es resulted from high levels<br />
of hunt<strong>in</strong>g and poach<strong>in</strong>g, as well as predation by<br />
wolves and bears across Europe, e.g. F<strong>in</strong>land [27] ,<br />
Figure 2.<br />
Change <strong>in</strong> Eurasian<br />
elk population<br />
abundance by<br />
decade and overall<br />
change between<br />
1964 and 2005. Please<br />
note that due to the<br />
way change was<br />
calculated, decadal<br />
change does not sum<br />
to overall change.<br />
61