130925-studie-wildlife-comeback-in-europe
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Scale Status Population trend Justification Threats<br />
Global<br />
[1]<br />
Least Concern Unknown Widespread<br />
Large population<br />
Largest population stable (Alps)<br />
Development<br />
Agriculture<br />
Exploitation<br />
Human disturbance<br />
Invasive species/genes<br />
Problematic native species<br />
Europe<br />
[12]<br />
Least Concern Unknown Widespread<br />
Large population<br />
Human disturbance<br />
Invasive species<br />
Largest population stable (Alps)<br />
Europe – tatrica:<br />
tatrica:<br />
tatrica:<br />
tatrica:<br />
regional<br />
Critically Decreas<strong>in</strong>g<br />
Very small population<br />
Interbreed<strong>in</strong>g<br />
populations<br />
Endangered<br />
[1]<br />
cartusiana:<br />
Projected cont<strong>in</strong>u<strong>in</strong>g decl<strong>in</strong>e<br />
cartusiana:<br />
Vulnerable<br />
Stable<br />
Interbreed<strong>in</strong>g<br />
cartusiana:<br />
Conf<strong>in</strong>ement to s<strong>in</strong>gle location<br />
Table 2.<br />
Summary of Global<br />
and European Red<br />
List assessments and<br />
threats listed for the<br />
Northern chamois.<br />
Table 3.<br />
Latest population<br />
estimates for the<br />
Northern chamois<br />
globally, <strong>in</strong> Europe<br />
and for European<br />
populations.<br />
The Balkan chamois (R. r. balcanica) is stable <strong>in</strong><br />
Bosnia-Herzegov<strong>in</strong>a, Croatia, Macedonia, Slovenia<br />
and Serbia, vulnerable <strong>in</strong> Albania, rare <strong>in</strong> Bulgaria<br />
and endangered <strong>in</strong> Greece [17] . Here, it is listed <strong>in</strong><br />
the Red Data Book of Threatened Vertebrates [18]<br />
and shoot<strong>in</strong>g has been banned s<strong>in</strong>ce 1969 [17] .<br />
Poach<strong>in</strong>g, which occurs both <strong>in</strong>side and outside<br />
protected areas, is considered the biggest threat<br />
but adventure tourism may be a grow<strong>in</strong>g problem<br />
<strong>in</strong> the future [17] .<br />
Abundance and distribution: changes<br />
As with many of the historical and 1950s/60s maps<br />
collected for this report, the 1955 distribution for<br />
the Northern chamois shown <strong>in</strong> Figure 1a is much<br />
coarser <strong>in</strong> resolution than the present day map [20] ,<br />
mak<strong>in</strong>g a comparison difficult. Although the best<br />
available, the 1955 distribution is mislead<strong>in</strong>g, as<br />
much of it falls mostly or entirely outside suitable<br />
Estimate Year assessed Reference<br />
Global Unknown -<br />
-<br />
Europe (based on below) 485,580 2004/5<br />
[19]<br />
% of global population -<br />
Austria 150,000 2004/5<br />
[19]<br />
Czech Republic 400 2004/5<br />
[19]<br />
Croatia 400 2004/5<br />
[19]<br />
France 62,500 2004/5<br />
[19]<br />
Germany 20,000 2004/5<br />
[19]<br />
Greece 800 2004/5<br />
[19]<br />
Italy 136,700 2004/5<br />
[19]<br />
Poland 80 2004/5<br />
[19]<br />
Romania 6,800 2004/5<br />
[19]<br />
Serbia 600 2004/5<br />
[19]<br />
Slovakia 600 2004/5<br />
[19]<br />
Switzerland 90,000 2004/5<br />
[19]<br />
Slovenia 15,600 1995<br />
[19]<br />
chamois habitat, and populations which were<br />
isolated at the time appear to be connected, giv<strong>in</strong>g<br />
the false impression of a large area of occupancy [20] .<br />
As such, the apparent reduction <strong>in</strong> range of over<br />
40% between 1955 and 2008 must not be taken at<br />
face value and <strong>in</strong>stead <strong>in</strong>terpreted with extreme<br />
caution, as it is likely an artefact of different<br />
map resolutions <strong>in</strong> time as opposed to a genu<strong>in</strong>e<br />
decl<strong>in</strong>e <strong>in</strong> range size [20] . The Northern chamois<br />
was, however, able to persist <strong>in</strong> most of the larger<br />
mounta<strong>in</strong> ranges, e.g. the central Alps, central<br />
D<strong>in</strong>aric, Carpathians and Sudetes, and southern<br />
Russia, and was even able to expand <strong>in</strong>to the Massif<br />
Central, Jura, Black Forest, parts of the Sudetes and<br />
very small populations <strong>in</strong> and around the D<strong>in</strong>aric<br />
mounta<strong>in</strong>s and southern Bulgaria (Figures 1a and<br />
b).<br />
In terms of abundance, Northern chamois<br />
populations <strong>in</strong> Europe have <strong>in</strong>creased by around<br />
90% over the period from 1960 and 2005, although<br />
this trend is not consistently positive <strong>in</strong> each<br />
decade (Figure 2). The trend is based on 10 populations<br />
from across Europe, represent<strong>in</strong>g a m<strong>in</strong>imum<br />
of 98,400 <strong>in</strong>dividuals or 20% of the total European<br />
population of 2004/5 and the data were from 44%<br />
of the countries of occurrence. Trend <strong>in</strong>formation<br />
was miss<strong>in</strong>g from a number of locations with<strong>in</strong><br />
the species’ current range, <strong>in</strong>clud<strong>in</strong>g the Massif<br />
Central <strong>in</strong> France, Germany, the Czech Republic, all<br />
of former Yugoslavia and Greece.<br />
Drivers of recovery<br />
Our analysis revealed no significant factors for<br />
either positive or negative abundance change.<br />
The decrease observed <strong>in</strong> the 1990s (Figure 2)<br />
can be attributed to populations from the Tatra<br />
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