130925-studie-wildlife-comeback-in-europe
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key tool for <strong>wildlife</strong> population <strong>in</strong>crease. Conflicts<br />
may be caused by the movement of <strong>wildlife</strong> <strong>in</strong>to<br />
adjo<strong>in</strong><strong>in</strong>g human-<strong>in</strong>habited areas (e.g. Brown<br />
bear <strong>in</strong> Slovenia and Wolver<strong>in</strong>e <strong>in</strong> Norway [129] ), but<br />
these can be offset by opportunities for <strong>wildlife</strong><br />
view<strong>in</strong>g and hunt<strong>in</strong>g (see above). On a local scale,<br />
exclusion or deterrence of <strong>wildlife</strong> can be highly<br />
effective. For example, electric fenc<strong>in</strong>g has been<br />
used to exclude bears from apiaries and small<br />
crop plantations [114, 131, 132] , keep wolves and lynx<br />
out of sheep graz<strong>in</strong>g fields [114] and mitigate crop<br />
damage [133, 134] .<br />
In areas where <strong>wildlife</strong> never really disappeared,<br />
traditional agricultural systems have persisted<br />
which provide techniques for limit<strong>in</strong>g livestock<br />
or crop damage. For example, <strong>in</strong> the Carpathians<br />
and parts of Italy, a long period of coexistence<br />
between humans and large carnivores has allowed<br />
both parties to coevolve by means of reciprocal<br />
ecological and behavioural adjustments [135] . For<br />
example, guard<strong>in</strong>g of livestock by dogs decreases<br />
the <strong>in</strong>cidence of livestock depredation [136, 137] , and<br />
employ<strong>in</strong>g local knowledge to avoid high-risk<br />
areas and conf<strong>in</strong><strong>in</strong>g livestock at night can also be<br />
highly effective [137] . Advocat<strong>in</strong>g and employ<strong>in</strong>g<br />
traditional techniques <strong>in</strong> areas where <strong>wildlife</strong> has<br />
recently returned may provide an effective tool for<br />
m<strong>in</strong>imis<strong>in</strong>g <strong>wildlife</strong> damage.<br />
Compensation schemes [138] are frequently used<br />
to offset livestock losses caused by predators, such<br />
as wolf, bear, lynx, and raptors [139, 140] (Table 1), and<br />
crop damage caused by large herbivores, cranes,<br />
ducks and geese [141, 142] . Where the relevant <strong>wildlife</strong><br />
species is not of conservation concern, occurs<br />
at higher densities or over a much larger area,<br />
and crop damage is more extensive, compensation<br />
schemes are likely to prove too costly and<br />
controll<strong>in</strong>g population densities by cull<strong>in</strong>g or<br />
regulated hunt<strong>in</strong>g becomes the primary route for<br />
m<strong>in</strong>imis<strong>in</strong>g conflict [143] . However, will<strong>in</strong>gness to<br />
pay for compensation schemes is likely to be <strong>in</strong>fluenced<br />
by a country’s wealth and demography (e.g.<br />
large sums of money spent on damage compensation<br />
schemes <strong>in</strong> the Netherlands [128] ).<br />
The ma<strong>in</strong> shortcom<strong>in</strong>g of compensation<br />
schemes is that they only address the outcome of<br />
human-<strong>wildlife</strong> conflict, though <strong>in</strong> some cases it<br />
is difficult to prevent or even m<strong>in</strong>imise conflicts<br />
<strong>in</strong> the first place (e.g. geese <strong>in</strong> grasslands). As a<br />
result, they are often costly and unsusta<strong>in</strong>able<br />
<strong>in</strong> the long run, or their cost-effectiveness is<br />
affected by the <strong>in</strong>tensity of the livestock regime<br />
(e.g. compensation may work <strong>in</strong> <strong>in</strong>tensively<br />
farmed livestock systems, but not <strong>in</strong> extensively<br />
farmed ones [116] ). They also often fail at creat<strong>in</strong>g<br />
positive attitudes towards <strong>wildlife</strong> [144] , yet are<br />
preferable to hav<strong>in</strong>g no system <strong>in</strong> place at all.<br />
Stewardship schemes provide ideal participatory<br />
approaches whereby people benefit from hav<strong>in</strong>g a<br />
healthy <strong>wildlife</strong> population, rather than receiv<strong>in</strong>g<br />
compensation when damage has happened. It is<br />
vital that we learn from experiences worldwide to<br />
devise the most appropriate schemes which allow<br />
coexistence of <strong>wildlife</strong> and people, and open up<br />
opportunities for local people to benefit from the<br />
presence of <strong>wildlife</strong>.<br />
Humans as part of nature:<br />
understand<strong>in</strong>g attitudes and<br />
establish<strong>in</strong>g participatory approaches<br />
<strong>in</strong> manag<strong>in</strong>g <strong>wildlife</strong> <strong>comeback</strong><br />
People are an <strong>in</strong>tegral part <strong>in</strong> many European<br />
landscapes and often come <strong>in</strong>to conflict with<br />
<strong>wildlife</strong>. Sometimes these conflicts can be a<br />
manifestation of oppos<strong>in</strong>g <strong>in</strong>terests between<br />
different stakeholders [145] , but commonly they are<br />
related to exist<strong>in</strong>g attitudes, culture, demography,<br />
feel<strong>in</strong>gs and levels of knowledge of the populace.<br />
Understand<strong>in</strong>g the social and economic issues<br />
<strong>in</strong>volved <strong>in</strong> human-<strong>wildlife</strong> conflicts, as well as the<br />
cultural and historical background, is therefore<br />
of utmost importance to develop a sound understand<strong>in</strong>g<br />
of the processes that form people’s<br />
attitudes towards <strong>wildlife</strong> [146, 147] .<br />
Worldwide, landscapes not only have a biological<br />
carry<strong>in</strong>g capacity to support return<strong>in</strong>g <strong>wildlife</strong>,<br />
but also a social carry<strong>in</strong>g capacity affected by<br />
emotions, attitudes and knowledge of people, such<br />
as the abundance of <strong>wildlife</strong> which is tolerated by<br />
the local <strong>in</strong>habitants [47] . Understand<strong>in</strong>g attitudes,<br />
beliefs and behaviours towards <strong>wildlife</strong> is vital<br />
<strong>in</strong> <strong>in</strong>creas<strong>in</strong>g cooperation and help<strong>in</strong>g parties to<br />
reach an optimal agreement or compromise <strong>in</strong> a<br />
participatory approach and ultimately may make<br />
the difference between a successful or unsuccessful<br />
conservation programme [148] . The level of<br />
exposure and distance to return<strong>in</strong>g <strong>wildlife</strong> has<br />
a direct bear<strong>in</strong>g on attitudes with<strong>in</strong> the human<br />
population [149] . For example, attitudes of urban<br />
citizens towards wolf <strong>comeback</strong> are generally<br />
positive as opposed to more negative attitudes<br />
held by rural <strong>in</strong>habitants [74, 150] . In Sweden, negative<br />
attitudes are stronger <strong>in</strong> areas with wolf populations<br />
than elsewhere [149, 151] . Impact of <strong>wildlife</strong> on<br />
personal <strong>in</strong>come is also important <strong>in</strong> shap<strong>in</strong>g<br />
perceptions: <strong>in</strong> Central Asia, local communities<br />
primarily rely<strong>in</strong>g on cash crops were more tolerant<br />
towards Snow leopards (Uncia uncia) than those<br />
rely<strong>in</strong>g on livestock [152] . In Poland, carp losses to<br />
otters were perceived as higher by private owners<br />
than by managers of state-owned fisheries [153] .<br />
However, <strong>in</strong> many cases negative attitudes are held<br />
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