P. Stahl et al., Predation on livestock by an expanding reintroduced lynx population: long-term trend and spatial variability, J APPL ECOL, 38(3), 2001, pp. 674-687
1. In recent decades, the Eurasian lynx Lynx lynx has recolonized former ha
bitat, bringing it into potential conflict with livestock. We studied the s
patial and temporal distribution of lynx attacks on sheep in the French Jur
a between 1984 and 1998, during and after its population expansion. We esti
mated the local and regional impact of lynx predation on livestock.
2. The number of attacks increased from three in 1984 to 188 in 1989, concu
rrently with the colonization of the main sheep range by lynx. During subse
quent years, 66-131 attacks were recorded annually (92-194 sheep killed per
year).
3. On average, 1.6 sheep were killed per attack. Lynx preyed disproportiona
tely on lambs and subadult sheep. A small percentage of flocks (9.5-22.9%)
were attacked, most of which (75.2%) were attacked once or twice a year. At
the regional level, annual sheep losses to lynx were 0.14-0.59% of the tot
al number of sheep.
4. The major lynx-livestock problem was due to clustered attacks in a few s
mall areas. Each year, two to six 'hot spots' (33-69% of the attacks) were
identified. Hot spots covered 0.3-4.5% of the total area where attacks occu
rred (1835-4061 km(2)). Roe deer abundance was higher in hot spots and, eve
n here, sheep only made up 3.1% of the lynx diet. These data show that lynx
were not killing sheep due to shortages of alternative prey or in response
to an increased need for food when rearing young.
5. The concentration of hot spots in only nine small areas between 1984 and
1998 indicated that only a few individual lynx were involved. The reappear
ance of hot spots at the same sites, after years of interruption and despit
e the removal of lynx, suggested that the ultimate factors causing hot spot
s were factors inherent to those sites. Further investigation is needed to
identify causal factors with a view to eliminating them. These may relate t
o landscapes features, animal husbandry practices or the behavioural ecolog
y of lynx.
6. In future, where large predator reintroductions are planned, the potenti
al for concentrated, localized, impact should be evaluated and mitigation m
easures put in place. For scattered and episodic lynx damage, financial com
pensation is the only realistic option at present. In hot spots, the cost-e
ffectiveness of guard-dogs or the selective removal of some individual lynx
should be evaluated.