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130925-studie-wildlife-comeback-in-europe

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Figure 1c.<br />

Map highlight<strong>in</strong>g<br />

areas of range<br />

expansion,<br />

persistence and<br />

contraction of the<br />

European bison <strong>in</strong><br />

Europe between 1971<br />

and 2008.<br />

Figure 2.<br />

Change <strong>in</strong> European<br />

bison population<br />

abundance by<br />

decade and overall<br />

change between<br />

1960 and 2005.<br />

Error bars have been<br />

removed for clarity.<br />

Please note that due<br />

to the way change<br />

was calculated,<br />

decadal change does<br />

not sum to overall<br />

change.<br />

% change<br />

3000<br />

2400<br />

1800<br />

1200<br />

600<br />

0<br />

<strong>in</strong> the wild. The abundance trend is based on 10<br />

populations from across the range, represent<strong>in</strong>g a<br />

m<strong>in</strong>imum of 1,200 <strong>in</strong>dividuals, or 44% of the total<br />

European population of 2011, cover<strong>in</strong>g 71% of all<br />

countries of occurrence. Data were miss<strong>in</strong>g from<br />

only two of locations with<strong>in</strong> the species’ current<br />

range, namely Romania and Lithuania.<br />

Drivers of recovery<br />

While no overrid<strong>in</strong>g factors could be identified <strong>in</strong><br />

our data set to expla<strong>in</strong> the large <strong>in</strong>crease <strong>in</strong> the<br />

European population of bison, it can undoubtedly<br />

be attributed to the large-scale breed<strong>in</strong>g, re<strong>in</strong>troduction<br />

and translocation efforts that have<br />

taken place s<strong>in</strong>ce its precipitous decl<strong>in</strong>e [1, 3, 4] and<br />

extirpation <strong>in</strong> the 20 th century. The first re<strong>in</strong>troduction<br />

took place <strong>in</strong> 1952 <strong>in</strong> the Białowieża forest<br />

and this population first started reproduc<strong>in</strong>g <strong>in</strong><br />

1957 [3] , which co<strong>in</strong>cides with the upward trend<br />

1960s 1970s 1980s 1990s 2000–05 1960–2005<br />

depicted <strong>in</strong> Figure 2. Changes <strong>in</strong> population size<br />

as well as genetic <strong>in</strong>tegrity are recorded <strong>in</strong> detail<br />

<strong>in</strong> the annually updated European Bison Pedigree<br />

Book (EBPB) [3] , which provides a central resource<br />

to guide re<strong>in</strong>troduction efforts. In addition to<br />

targeted management, environmental conditions<br />

such as w<strong>in</strong>ter snow cover and May temperature<br />

have been shown to affect the bison <strong>in</strong> Białowieża<br />

forest, with less snow and warmer temperatures<br />

result<strong>in</strong>g <strong>in</strong> higher recruitment rates [2] . The species<br />

also benefits from oak seed mast years, which<br />

provide an abundance of food, and the protection<br />

and management of oak forest should therefore be<br />

more heavily <strong>in</strong>tegrated <strong>in</strong>to bison management [2] .<br />

However, while the bison may <strong>in</strong>deed have a<br />

more favourable conservation status at present,<br />

the exponential recovery <strong>in</strong> abundance observed<br />

must be considered <strong>in</strong> the context of the severely<br />

depleted state of the population <strong>in</strong> 1960. Interest<strong>in</strong>gly,<br />

there has also not been a concomitant<br />

clear expansion <strong>in</strong> range. While new territories<br />

have been established across eastern Europe,<br />

the species’ distribution has rema<strong>in</strong>ed small and<br />

fragmented. In addition, re<strong>in</strong>troductions appear to<br />

have been los<strong>in</strong>g their momentum [3] , which could<br />

expla<strong>in</strong> the larger <strong>in</strong>creases <strong>in</strong> earlier decades.<br />

Overall, successive re<strong>in</strong>troductions have not yet<br />

resulted <strong>in</strong> an <strong>in</strong>crease <strong>in</strong> the range of the species<br />

or the viability of exist<strong>in</strong>g herds [5] . Recommendations<br />

for future conservation efforts are to focus on<br />

creat<strong>in</strong>g suitable habitat <strong>in</strong> areas where farmland<br />

is be<strong>in</strong>g abandoned, such as <strong>in</strong> the Carpathians [5] ,<br />

as well as on establish<strong>in</strong>g a metapopulation across<br />

eastern Europe, on which the long-term survival of<br />

the species depends [21] .<br />

28

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