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130925-studie-wildlife-comeback-in-europe

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Figure 1b.<br />

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

areas of range<br />

expansion,<br />

persistence and<br />

contraction of the<br />

Wolver<strong>in</strong>e <strong>in</strong> Europe<br />

between 1955 [31]<br />

and 2009–12 [2, 18] .<br />

Please note that the<br />

contraction observed<br />

from 1955 to 2012<br />

is likely to be an<br />

artefact of the<br />

difference <strong>in</strong> map<br />

resolution caused<br />

by a disparity <strong>in</strong><br />

the accuracy of<br />

the methods used.<br />

Expansions <strong>in</strong><br />

southern Norway<br />

are likely to be<br />

overestimations<br />

result<strong>in</strong>g from the use<br />

of range <strong>in</strong>formation<br />

compris<strong>in</strong>g areas of<br />

sporadic occurrence<br />

<strong>in</strong> which the species<br />

is culled.<br />

Wolver<strong>in</strong>e now occupies approximately 1,938,000<br />

km 2 , which is just under 40% of its historical distribution<br />

(Figure 1a).<br />

The recent positive change <strong>in</strong> distribution is<br />

also reflected <strong>in</strong> the abundance trend of monitored<br />

Wolver<strong>in</strong>e populations. The species shows a steady<br />

<strong>in</strong>crease of approximately 270% over the 26-year<br />

period between 1979 and 2005, with a doubl<strong>in</strong>g <strong>in</strong><br />

number <strong>in</strong> the 1990s (Figure 2). The trend, which<br />

starts <strong>in</strong> the late 1970s due to non-availability of<br />

data before this po<strong>in</strong>t <strong>in</strong> time, is based on 19 populations<br />

from Norway, Sweden, F<strong>in</strong>land and Russia,<br />

represent<strong>in</strong>g a m<strong>in</strong>imum of 245 <strong>in</strong>dividuals or 9%<br />

of the total European population from 2009–12. It<br />

should be noted, however, that this Figure is likely<br />

to be an underestimate, as most of the populations<br />

used density measures, which are unusable for<br />

estimat<strong>in</strong>g the m<strong>in</strong>imum number of <strong>in</strong>dividuals<br />

represented. In addition, exist<strong>in</strong>g estimates may<br />

not be reliable for this hard-to-monitor species.<br />

because these bounties were paid per <strong>in</strong>dividual,<br />

and den sites were often easier to f<strong>in</strong>d. Legal<br />

protection, which started <strong>in</strong> Sweden <strong>in</strong> 1969 and<br />

was gradually established <strong>in</strong> Norway between 1973<br />

and 1983 [8, 29] , has therefore played a major role <strong>in</strong><br />

the recent <strong>comeback</strong> of the species. It has resulted<br />

<strong>in</strong> <strong>in</strong>creases <strong>in</strong> the populations of both countries [8] ,<br />

and allowed the Wolver<strong>in</strong>e to spread naturally <strong>in</strong>to<br />

the forested landscapes from which it had been<br />

extirpated <strong>in</strong> Sweden [28] .<br />

However, divergent management strategies<br />

have led to differ<strong>in</strong>g rates of recovery <strong>in</strong> the two<br />

countries. In Norway, the species is publicly hunted<br />

us<strong>in</strong>g generous quotas, and there is extensive lethal<br />

control <strong>in</strong> certa<strong>in</strong> regional management zones [4] .<br />

Some areas <strong>in</strong> the southwest follow a zero tolerance<br />

rule regard<strong>in</strong>g Wolver<strong>in</strong>e breed<strong>in</strong>g to m<strong>in</strong>imise<br />

conflict with sheep husbandry, which reduces the<br />

probability of reproduction by 25 times compared<br />

Figure 2.<br />

Change <strong>in</strong> Wolver<strong>in</strong>e<br />

population<br />

abundance by<br />

decade and overall<br />

change between<br />

1979 and 2005.<br />

Please note that<br />

for this species,<br />

95% confidence<br />

limits could not be<br />

calculated.<br />

Drivers of recovery<br />

300<br />

The gradual range expansion and population<br />

<strong>in</strong>crease observed <strong>in</strong> Europe s<strong>in</strong>ce the 1960s can<br />

be expla<strong>in</strong>ed by a number of reasons discussed<br />

<strong>in</strong> the literature. Much of the <strong>in</strong>itial contraction<br />

observed <strong>in</strong> the Wolver<strong>in</strong>e from the mid-19 th<br />

century (Figure 1a) can be attributed to human<br />

persecution due to livestock depredation [4, 8, 29] ,<br />

which was re<strong>in</strong>forced by a bounty payment system.<br />

The impact was primarily on females with cubs<br />

% change<br />

240<br />

180<br />

120<br />

60<br />

0<br />

1960s 1970s 1980s 1990s 2000–05 1979–2005<br />

123

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