LEGOUAR P, SCHEKKERMAN H, JEUGD H VAN DER, NOORDWIJK A VAN, STROEKEN P, HARXEN R VAN & FUCHS P (2010) Survival and dispersal in Little Owls Athene noctua in The Netherlands based on 35 years of ringing data. LIMOSA 83 (2): 61-74.
The breeding population of Little Owl in The Netherlands
has decreased by 50-70% over the past 50 years. Loss of
suitable habitat and a reduction in breeding success have
been indicated as the main causes of this decline. Here,
we analyse ringing data from the period 1973-2007 (Fig.
1) to evaluate whether low or declining survival may have
contributed as well. We used multi-state mark-recapture
modelling to jointly analyse live recaptures and dead recoveries
of a total of 25,759 ringed Little Owls (of which
3,812 were reported back at least once), taking into account
spatial variation in ringing and recapture effort between
and within two main regions (Fig. 2).
Adult annual survival rate was on average 75.3%
(95%-CL 69-82%), did not differ between regions and
showed no long-term trend but was usually high with
markedly lower values in about 25% of all years (Fig. 5a).
Poor survival years seemed to occur regularly with a period
of three to four years but were not associated with
variation in the abundance of voles, winter severity index
or duration of snow cover. They were associated with
lower than average mean annual temperature and rainfall
(Fig. 6), which may have affected availability of
arthropod prey and earthworms. While adult mortality
was spread throughout the year with a slight peak during
the breading season, mortality of juveniles peaked
shortly after fledging (Fig. 3). Collision with road traffic
was the most frequently reported cause of death (Fig. 4).
First-year survival was on average 25.8% (95%-CL
22-30%) and declined from 30% in the beginning to 18%
at the end of the study period (Fig. 5 lower panel). This
decline was not well explained by variation in mortality
of nestlings after ringing, an increase in road traffic, variation
in weather conditions or vole abundance. We hypothesize
that a general deterioration of feeding conditions
may have played a role, which may also underlie
the decline in breeding success reported by Stroeken et
al. (2009). Both reduced first-year survival and declining
productivity will have contributed to the observed population
decline over the past 20 years, while an earlier
strong decline in the 1970s was probably mainly caused
by direct loss of nesting habitat through land consolidation
and country-wide destruction of orchards.
Data on dispersal distances, corrected for the spatial
distribution of observer effort, confirmed the Little Owl's
highly resident behaviour, with 76% of adults breeding
at the same coordinates as (i.e. within c. 1 km from) the
previous year and 15% of young recruits settling within
this distance from the natal site. Natal dispersal (95%
within 10 km) was more prominent than breeding dispersal
(95% within 4 km), and females recruited further
away than males (Fig. 7).
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