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The Greenland White-fronted Goose Anser albifrons flavirostris

The Greenland White-fronted Goose Anser albifrons flavirostris

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social system has traditionally regulated recruitment<br />

into the reproductive classes in the <strong>Greenland</strong><br />

<strong>White</strong>-<strong>fronted</strong> <strong>Goose</strong> population, but it is<br />

tempting to speculate this was and remains the<br />

case. <strong>The</strong> population is characterised by unusually<br />

prolonged parent-offspring relationships<br />

(25% were still associated with one parent in their<br />

seventh winters, MS 11), even compared to other<br />

races of <strong>White</strong>-<strong>fronted</strong> Geese (Ely 1993). Yet the<br />

production of young per successfully breeding<br />

female (measured by family brood size on the<br />

wintering grounds) is unusually high compared<br />

to most other goose populations, consistent with<br />

the idea that only the highest quality pairs breed<br />

in any one year. <strong>The</strong>se features are consistent with<br />

a social system that enables successful pairs to<br />

maintain high social status through persistent<br />

association of earlier offspring, which seem likely<br />

to remain with their extended families because<br />

of the high relative cost of pairing and losing such<br />

status. Reproduction in the population as a whole<br />

therefore involves a relatively low proportion of<br />

the potentially reproductively active individuals<br />

- generally only those of high quality (see Figure<br />

9.1 and 9.2 above).<br />

Under legislative protection from shooting on the<br />

winter quarters, the population has shown an<br />

increase consistent with constant adult survival<br />

and observed breeding success rates. If some density<br />

dependent function were involved, whereby<br />

the overall number of opportunities to nest in any<br />

one year were limited to the same number every<br />

year, it might be expected that, above this threshold<br />

level, entry into the breeding class would be<br />

severely limited. <strong>The</strong>re is now some emerging<br />

evidence to suggest that such a limit exists for<br />

the <strong>Greenland</strong> <strong>White</strong>-<strong>fronted</strong> <strong>Goose</strong>. Amongst<br />

those wintering at Wexford and Islay (some 60%<br />

of the total population), the number of successfully<br />

breeding pairs returning with young steadily<br />

increased during the 1970s, although production<br />

in any one year varied with summer temperature<br />

in <strong>Greenland</strong> (Figure 9.3). Since protection<br />

from hunting, the absolute number of successful<br />

breeders has been stable at c.1,000 pairs<br />

in years when cold summer conditions have not<br />

limited successful breeding (Figure 9.3). <strong>The</strong>re<br />

does seem therefore to be a current limit to the<br />

number of pairs that can breed successfully<br />

amongst birds using these two wintering resorts<br />

(chapter 6). This is manifest amongst the marked<br />

population in falling recruitment levels amongst<br />

cohorts hatched since 1984, partly a result of delayed<br />

age of first breeding amongst this sample<br />

Number of successful breeding pairs at<br />

Islay and Wexford combined<br />

1200<br />

1000<br />

800<br />

600<br />

400<br />

200<br />

mild springs<br />

cool springs<br />

0<br />

1965 1970 1975 1980 1985 1990 1995 2000<br />

Figure 9.3. Total number of successfully breeding pairs<br />

(i.e. parents returning with at least one young) in autumn<br />

from Islay and Wexford combined. Open symbols<br />

are years with cooler than average June temperature<br />

in West <strong>Greenland</strong>, solid symbols warmer than<br />

average (based on data from Zöckler & Lysenko (2000).<br />

Note the apparent constant maximum number of successful<br />

breeding pairs since protection (arrow) in seasons<br />

of above average summers.<br />

but also declining brood size amongst those that<br />

breed (chapter 6).<br />

<strong>The</strong> demographic data support the idea that there<br />

is an apparent current 'ceiling' to reproductive<br />

output in this population, but it is far from clear<br />

how this limitation is exercised. <strong>The</strong>re might be a<br />

limit to the extent of breeding habitat or number<br />

of nest sites, but these seem highly unlikely, given<br />

the wide extent of available habitat (chapter 6).<br />

Furthermore, the limit could be to brood rearing<br />

nursery habitat, or to the post fledging survival<br />

of young. Both of these factors also seem highly<br />

unlikely, given that a density dependent mechanism<br />

would tend to reduce brood size (for example,<br />

as a result of losses of smallest goslings Owen<br />

& Black 1989), rather than result in a loss of entire<br />

broods from the population. In the <strong>Greenland</strong><br />

<strong>White</strong>front, a characteristically low proportion of<br />

successful breeders return with unusually large<br />

families compared to other geese populations.<br />

Hence, it would therefore appear that relatively<br />

few pairs attempt to breed in any one year, and<br />

amongst those pairs which do, the majority breed<br />

successfully, in terms of raising large numbers of<br />

young per family that survive to reach the wintering<br />

grounds. As discussed above, this could<br />

be the result of density-dependent limitation in<br />

access to nutrient acquisition on the wintering<br />

grounds, the Iceland spring staging areas, in<br />

<strong>Greenland</strong> during pre-nesting feeding or a combination<br />

of all three. Since the extended family<br />

relationships persist on the wintering, spring stag-<br />

77

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