Ecology, Conservation and Management of Wild Pigs and Peccaries

(Axel Boer) #1

339


Chapter

31


Wild Boar Management in Europe:


Knowledge and Practice


András Náhlik, Seán Cahill, Sandra Cellina, János Gál, Ferenc Jánoska, Carme Rosell,
Sophie Rossi, and Giovanna Massei

Introduction


Wild boar (Sus scrofa) is a widely distributed species native to
Eurasia that is expanding its range through the spontaneous
colonization of new areas, recolonization of former territories
it once inhabited, or through intentional and unintentional
introduction of the species by humans (Massei et  al. 2015).
It primarily inhabits temperate and tropical forests, but it
also inhabits semi-arid, taiga, and mountain areas from oce-
anic to continental climates as well (Spitz 1999; Powell 2004).
Its range in Europe covers almost the entire continent, with
high densities in areas with good-quality habitats. It has been
spreading north towards eastern Fennoscandia for more than
40 years (Erkinaro et al. 1982). Recently it has been expanding
its territory to the north-west, and it is expected to eventually
colonize the coastal territory of Norway (Rosvold & Andersen
2008). In the United Kingdom and Denmark, the species has
become re-established following farm escapes (Andersen &
Holthe 2010; Wilson 2014). The predicted distribution range
of wild boar on the basis of climatic suitability data estimated
for the present time covers the current distribution range fairly
well and is even able to predict the most likely areas for new
colonization such as Finland and Sweden (Vilaça et al. 2014)
(Figure 31.1).
With annual increases in population that may exceed
100 per cent, wild boar possess the highest reproductive rate
among ungulates (Bieber & Ruf 2005). An r-selection strategy
that includes a high reproductive rate makes it difficult to man-
age wild boar populations. However, as mentioned by Allendorf


et al. (2008), harvest regulations have the potential to cause the
loss of genetic variation in wild boar. Furthermore, a series of
other undesirable processes were reported as a consequence of
misguided harvesting such as altering the population structure
through selective hunts, enlarging the proportion of juveniles
that are capable of reproducing early (Gamelon et al. 2011), and
increasing the population density (Massei et al. 2015). In turn,
the latter has the potential to increase the disease risk (Gortázar
et al. 2006), to modify the ecosystem (Hobbs 1996), to gener-
ate conflict with human land-use areas leading to economic
damage (Cozzi et al. 2015), and to raise the number of animal–
vehicle collisions (Zuberogoitia et al. 2014). In addition to all of
this, the urbanization process of the species coincided fairly well
with the expanding populations both in distributional range
and in numbers (Cahill et al. 2012).

Population Trends and Influential Factors
in Europe
Wild boar population has increased steadily across Europe since
the beginning of the 1980s. This statement is supported by the
increasing trend of hunting bags paralleled by a simultaneous
growth in the number of vehicle collisions and agricultural dam-
age caused by wild boar. According to the review by Massei et al.
(2015), a minimum of 2.2 million wild boar were harvested across
the 18 investigated countries, compared to about 864,000 har-
vested in 1992. If the remaining countries that were not included
in this analysis were added, the total number of wild boar annu-
ally harvested in Europe would be in excess of three million.

Unsuitable
Suitable

Figure 31.1 Distribution range of wild
boar (Sus scrofa) in Europe, as predicted
on the basis of climatic suitability data
estimated for the present time (from
Vilaça et al. 2014).

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