Ecology, Conservation and Management of Wild Pigs and Peccaries

(Axel Boer) #1
Part II: Species Accounts

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high passage rate through the digestive tract (Schley & Roper
2003). The diet of wild boar often contains other uncommon
food items including biological materials such as algae, as well
as garbage or inorganic material like plastic, rubber and stones
(Ballari & Barrios-García 2014). In some cases, these materi-
als are incidentally ingested during rooting or surface foraging.
Beyer et al. (1994) estimated that 2.3 per cent of wild boar diet
consisted of soil.
The data from published literature allowed grouping of
the results of the analyses of wild boar diet according to four
habitat types, i.e. forest–farmland, large mixed lowland forests,
wetlands, and mountains (Figure 21.8). In terms of quality, five
categories of fodder were distinguished. These included agri-
cultural crops, soft and hard mast, as well as animal food, all of
which contain high levels of metabolic energy (15.2–15.8 kJ/g
dry weight). It also included roots, ground flora, and browse,
whose nutritional value amounts to 14.3 kJ/g dry weight and

7.1 kJ/g dry weight, respectively (van Wieren 2000; Hodgkinson
et al. 2008; Śliwiński et al. 2010).
The multi-annual and seasonal variability of the diet of wild
boar was studied in the forest–farmland habitat of Luxembourg
(Cellina 2008; Figure 21.9). For three subsequent years, the
proportion of natural food (ground flora, browse, roots, and
animals) was highest in the spring. In the summer season, agri-
cultural crops predominate (50–65 per cent). Hunter-provided
supplemental food was important to wild boar in the autumn
and winter. During a heavy mast year (2004), the importance of
the category of supplemental food dropped while the proportion
of oak and beech seeds increased to 58.6 per cent (Figure 21.9).
Annual diet. According to Genov (1981a), Dardaillon
(1987), Herrero et al. (2006) and Gimenez-Anaya et al. (2008),
agricultural crops predominated in the year-round diet of the
wild boar living in Polish and Spanish forest–farmland habitat
(79 per cent) and in the wetlands situated on the western coast of

Figure 21.9 The proportions of food
components (per cent of volume) in
the diet of 1200 wild boar bagged
from the spring of 2003 to the summer
of 2005 in forest–farmland habitat in
Luxembourg (from Cellina 2008).

Figure 21.8 The proportions of
particular food categories in the
year-round diet of wild boar in different
types of habitat (1) forest–farmland
(Genov 1981b; Herrero et al. 2006);
(2) large mixed lowland forests (Abáigar
1993; Groot Bruinderink et al. 1994;
Fournier-Chambrillon et al. 1995);
(3) wetlands (Dardaillon 1987; Gimemez-
Anaya et al. 2008) and (4) mountain
areas (Baubet et al. 2004; Kodera et al.
2013).

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