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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 />

296

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