M. Frederiksen et al., The interplay between culling and density-dependence in the great cormorant: a modelling approach, J APPL ECOL, 38(3), 2001, pp. 617-627
1. The population of great cormorants Phalacrocorax carbo sinensis breeding
in northern Europe has increased from 5000 pairs around 1970 to c. 100 000
pairs in the late 1990s, leading to serious conflicts with fishery and aqu
aculture interests. Management action, including widespread culling, has be
en taken in several countries.
2. Since 1990, presumed density-dependent declines in demographic performan
ce have appeared in cormorant populations. We employed an extended Leslie m
atrix model to study the interaction between culls and density-dependence i
n regulating breeding and autumn population sizes, with emphasis on evaluat
ing the effects of culling.
3. During 1979-92, the breeding population of great cormorants in northern
Europe increased by 18% year(-1), in accordance with observed life-cycle pa
rameters before the appearance of density-dependent declines.
4. We modelled six scenarios with varying assumptions about the strength of
density-dependence in adult survival and the proportions of breeding cormo
rants. A series of cull estimates was also included. Scenarios with moderat
e or strong levels of density-dependence provided predictions that fit the
observed numbers of breeding pairs, whereas scenarios without density-depen
dence in survival overestimated real population growth.
5. The most well-supported scenarios indicated that the effect of culls at
the present level (1998-99: 17 000 cormorants shot) was limited (< 10% redu
ction at equilibrium). Increasing the annual cull to 30 000 still had a lim
ited effect, whereas shooting 50 000 birds year(-1) led to population extin
ction within 20-40 years. Shooting a fixed proportion of the population exc
eeding a threshold, through density-dependent culling, could eliminate diff
erences among scenarios and stabilize the population.
6. We conclude that culls probably have had a limited effect on cormorant p
opulations, but if carried out in a density-dependent way they could stabil
ize numbers near a desired level. However, a reduction in the number of cor
morants may not lead to a similar reduction in conflicts, and actions to co
ntrol damage rather than cormorant populations are likely to be more cost-e
ffective. If culling is to be continued, we recommend the adoption of an ad
aptive and co-ordinated management strategy across Europe. We also advocate
the need to account for density-dependent mechanisms in general culling st
rategies.