KOFFIJBERG K, COTTAAR, F & JEUGD H VAN DER (2006) Increase of Lesser White-fronted Geese Anser erytrophus in the Netherlands in 1989-2005. LIMOSA 79 (3): 107-122.
A dataset with 2500 observations and 2150
colour-ring resightings of 164 marked individuals
were analysed to assess numbers, distribution,
use of staging sites and origin of Lesser
White-fronted Geese in The Netherlands in
1989-2005. Historical data and records published
by the Dutch rarities committee from before
1989 suggest that small numbers of
Lesser-White fronted Geese were present in
the Netherlands in December-February. This
pattern changed after re-introduction of Lesser
White-fronted Geese in Swedish Lapland from
1981 onwards (Fig. 1). Especially since the mid
1990s numbers increased steadily, to about
120 individuals in recent winters (Fig. 2).
Today, highest numbers are observed from
mid-October to mid-March (Fig. 6). First arrivals
are reported in September. Observations
in late spring coincide with departures of
Barnacle and Dark-bellied Brent Geese in the
northern part of the country in the 2nd half of
May.
In six areas traditional staging sites have been
established (Fig. 3), supporting 87% of all observations
since 1989/90. Anjumerkolken, near
the Lauwersmeer area in northern Friesland, is
the oldest known staging area. Up to 80 individuals
have been counted here (Fig. 4) and
usually at least 50% (sometimes up to 75%) of
the seasonal maximum in the Netherlands concentrates
in this area (Fig. 5). This pattern is
confirmed by sightings of colour-ringed birds,
of which 60% have been reported from
Anjumerkolken. Other traditional sites are
Oudeland van Strijen, Korendijksche Slikken,
Polder Biert (all Zuid-Holland), Petten (Noord-
Holland) and Doniaburen (Friesland). The latter
site is characterized by a high turnover: staging
numbers never exceeded 8 individuals, but
40 different colour-ringed individuals have
been reported here. This also applies to Den
Bommel (Zuid-Holland), where Lesser Whitefronted
Geese are recorded irregularly, but
again many different individuals (40) are involved.
Initially, distribution of Lesser White-fronted
Geese in the Netherlands mirrored the traditional
staging sites their foster-parents
(Barnacle Geese), around the Wadden Sea,
in Friesland and in the Haringvliet area in SW-Netherlands. Anjumerkolken was the first
site where Lesser White-fronted Geese have
been reported regularly, from 1983/84 onwards.
Still, many sightings of colour-ringed individuals
(i.e. the original re-introduced individuals)
originate from traditional Barnacle Goose
staging areas (Fig. 8). Of 58 ringed individuals
that were known to accompany other geese,
34 (59%) were associated with Barnacle
Geese. Unringed birds on the other hand,
which involve mainly offspring of the re-introduced
birds and perhaps also small numbers
of birds of wild origin, are also reported from
other parts of the country and often associate
with flocks of Greater White-fronted Geese. Of
43 birds recorded in flocks of Greater Whitefronts,
only 8 (19%) were marked. This indicates
that the originally re-introduced birds still
follow the traditions of their foster-parents,
whereas their offspring also explore new staging
sites and mix up with other goose species.
Numbers and sightings of colour-rings point
out that first arrivals in autumn stay some time
in the Anjumerkolken area before moving on to
wintering areas in Noord- en Zuid-Holland in
November-December (Tab. 1). Exchange between
the wintering sites is rather low, even if
some of these sites are only up to 20 km apart.
This suggests that the majority of the Lesser
White-fronted Geese are faithful to their wintering
sites, and mainly meet at staging sites en
route, like Anjumerkolken, or also in
Doniaburen; Petten and Den Bommel. At several
sites, flocks of Lesser White-fronted Geese
are reported to prefer specific parts of the
staging area, often pastures with hummocks or
along ditches. In spring, again many Lesser
White-fronted Geese pass Anjumerkolken on
their way to the breeding areas, but numbers
are lower than in autumn, probably because
the time span of spring migraton is longer.
According to sightings of colour-rings and the
numbers observed, the wintering population in
the Netherlands mainly represents the re-introduced
Swedish population, i.e. both the released
birds and their offspring. From all
known individuals ringed after 1994/95 (92), 77
(84%) were observed at least once in the
Netherlands. Considering an annual mortality
of about 7% (preliminary calculations with
MARK, using the available database with sightings),
this means that nearly all Swedish birds
stay in the Netherlands in winter. Hence, the increase
of wintering Lesser White-fronted
Geese in the Netherlands is mainly result of the
increase of the re-introduced population in
Swedish Lapland. However, numbers observed
in recent winters are about 20 individuals
higher than estimates for the Swedish
breeding population. This might indicate that
this estimate is below the actual population
size, e.g. because not all breeding sites are
known or birds have meanwhile settled outside
Sweden. That 16 out of 22 ringed Lesser Whitefronted
Geese were never observed in Sweden
but were reported in winter in the Netherlands
supports this hypothesis. Moreover, we cannot
exclude that also birds of different origin are
present in the Netherlands, similar to the situation
before re-inroductions in Sweden started.
Two observations of re-introduced Finnish
birds (in January 2003 and December 2004) fit
in this context. To what extent wild birds are involved
is not clear. Observations of Lesser-
White-fronted Geese in flocks of Greater Whitefronted
Geese might possibly involve breeding
birds of Russian origin. The current known migration
route from Fennoscandia to SE-Europe,
as retrieved by satellite telemetry, is situated
about 450 km east of the border with Germany.
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