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<strong>Fennoscandian</strong> <strong>Lesser</strong> <strong>White</strong>-<strong>fronted</strong> <strong>Goose</strong> <strong>conservation</strong> <strong>project</strong> – Annual report 1999<br />

Aarvak & Øien: Monitoring of staging <strong>Lesser</strong> <strong>White</strong>-<strong>fronted</strong> Geese at the Valdak Marshes in 1999<br />

disturbance from local people picking cloudberries (Rubus<br />

chamaemorus). As a result, the geese spend the daytime on the<br />

adjacent small islands in the innermost part of the Porsangen Fjord.<br />

The LWfG have also been observed on the small islets Kråkholman<br />

at the boundary of Stabbursnes Nature Reserve (in 1996) and the<br />

northwest point of the Oldereidnesset Peninsula (in 1997).<br />

3.3. Breeding success<br />

A total of 26 adults and 17 (40 %) juveniles were registered during<br />

the autumn monitoring period. Six pairs brought goslings, yielding<br />

a mean brood size of 2.8 (Tables 2 and 4). On the Skjåholmen Island,<br />

only one pair with two young were seen (see Tolvanen 2000, pp.<br />

28–31 in this report).<br />

Breeding success is monitored during post breeding period at the<br />

Valdak Marshes, which represent the first staging area before the onset<br />

of autumn migration. The observations of brood sizes may explain the<br />

variation in the breeding success between years. Mean brood size<br />

observed at the Valdak Marshes in the years 1994–1999 is as high as 3.2<br />

26<br />

Photo. In spring 1999, 22 adult <strong>Lesser</strong> <strong>White</strong>-<strong>fronted</strong> <strong>Goose</strong> pairs<br />

were staging at the Valdak Marshes, which is 11 pairs less than<br />

in the previous year. The picture shows a pair of LWfG at the<br />

Valdak Marshes in May 1999. © Ingar Jostein Øien<br />

Table 2. Autumn age ratio and annual brood sizes of <strong>Lesser</strong> <strong>White</strong><strong>fronted</strong><br />

Geese in the years 1981-1999, based on counts during autumn<br />

migration at the Valdak Marshes (see also Table 4 for distribution of<br />

broods and number of pairs with broods). No data from the years<br />

1982–1986, 1988–1991 and 1993.<br />

Year n n n % n Mean Mean Mean<br />

ad juv total juv flocks brood1 brood2 brood3 1981 10 18 28 64.3 1 3.6<br />

1987 10 18 28 64.3 1 3.6<br />

1992 24 34 58 58.6 ? 2.8<br />

1994 31 33 64 *51.6 3 2.4 2.2 1.3<br />

1995 61 67 128 52.3 3 3.9 2.2 2.7<br />

1996 16 23 39 59.0 1 2.6 2.9 1.0<br />

1997 25 32 57 56.1 1 4.0 2.6 1.2<br />

1998 29 31 60 51.6 3–1 2.8 2.4 0.9<br />

1999 26 17 43 39.5 6 2.8 1.3 0.8<br />

1 Counts of pairs with broods in autumn.<br />

2 Number of juveniles divided by number of adults (pairs) in autumn.<br />

3 Number of juveniles in autumn divided by number of pairs in spring.<br />

* Assumed that the observations are from three independent flocks.<br />

Table 3. Overview of the autumn staging period at the Valdak Marshes<br />

in the years 1981-1999 (all observations are from the period 16 August<br />

– 10 September).<br />

Year Observation dates (extremes) Time span<br />

First Last Occasional in days<br />

1981 17 Aug (1)<br />

1987 20 Aug (1)<br />

1992 18 Aug 20 Aug (3)<br />

1994 17 Aug 10 Sep 25<br />

1995 19 Aug 06 Sep 19<br />

1996 22 Aug 05 Sep 15<br />

1997 20 Aug 03 Sep 15<br />

1998 17 Aug 02 Sep 17<br />

1999 16 Aug 03 Sep 19<br />

(sd=1.4, n=58), although it varies significantly between years (Aarvak<br />

et al. 1997). It thus seems that the production is generally high, when<br />

based only on the individuals seen on post-moult.<br />

Estimates on brood size can be derived in different ways.<br />

Probably, the best estimate is based on the number of juveniles<br />

compared with the number of pairs observed (potential breeders) in<br />

the pre-breeding period (Mean brood 3 - cf. Aarvak et al. 1997), which<br />

yields an estimate of 0.8 goslings per potential breeding pair for<br />

1999. This estimated 0.8 goslings fledged per potential breeding pair<br />

yield a ratio of 29.3% juveniles in the autumn/winter population<br />

based on the number of juveniles produced during summer in relation<br />

to all birds that were present at Valdak in spring. For the years 1994,<br />

1995, 1996, 1997 and 1998 we obtained an estimated proportion of<br />

37.1%, 52.8%, 29.1%, 35.2% and 27.0% respectively, with a mean<br />

for all years of 35.1% (sd=9.5).<br />

Many studies on arctic breeding geese like Barnacle <strong>Goose</strong> (Branta<br />

leucopsis), Brent <strong>Goose</strong> (B. bernicla), <strong>White</strong>-<strong>fronted</strong> <strong>Goose</strong> (Anser<br />

albifrons) and Tundra Bean <strong>Goose</strong> (A. fabalis rossicus) use the age<br />

composition (first-winter<br />

individuals and adults) during<br />

mid winter counts as a measure<br />

of the breeding success of the<br />

preceding breeding season (e.g.<br />

Ebbinge 1991). In contrast to<br />

what we have found in the<br />

LWfG, these studies show that<br />

the proportion of juveniles varies<br />

heavily between 0 and 60% for<br />

Brent <strong>Goose</strong>, 5–30% for<br />

Barnacle <strong>Goose</strong> and 2–50% for<br />

<strong>White</strong>-<strong>fronted</strong> <strong>Goose</strong> (Ebbinge<br />

1989, Ebbinge 1991, Fox &<br />

Photo. During the autumn staging period, the <strong>Lesser</strong> <strong>White</strong>-<strong>fronted</strong> Geese spend more on the islets in the<br />

inner part of the Porsangen Fjord than at the Valdak Marshes. © Ingar Jostein Øien, June 1997<br />

Gitay 1989).

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