The Greenland white‐fronted goose Anser albifrons flavirostris in Ireland and Britain 1982/83–1994/95: Population change under conservation legislation

• Published in: Wildlife Biology
• Main Authors: Fox, Anthony D., Norriss, David W., Stroud, David A., Wilson, H. John, Merne, Oscar J.
• Other Authors: World Wildlife Fund
• Format: Article in Journal/Newspaper
• Language: English
• Published: Wiley 1998
• Subjects: Greenland; Islay
• Online Access: http://dx.doi.org/10.2981/wlb.1998.010; https://onlinelibrary.wiley.com/doi/full-xml/10.2981/wlb.1998.010; https://onlinelibrary.wiley.com/doi/pdf/10.2981/wlb.1998.010

After protection from hunting on the wintering range in 1982/83, complete surveys of Greenland white‐fronted geese at all known Irish and British wintering resorts have been carried out annually. These showed that this population increased by 5.0% per annum from 16,541 in spring 1983 to 30,459 in spring 1995, characterised by a 6.6% annual increase during 1982/83–1991/92, followed by a less rapid increase in subsequent years. In addition, regular counts of at least eight wintering flocks also exist prior to 1982/83. Five of these (including the two most important, Islay in Scotland and Wexford in Ireland) showed no trend before protection, but significant increases after legislation. Two other flocks at protected sites showed increasing numbers prior to changes in legislation, followed by stable numbers afterwards and the eighth flock increased in number before and after protection. On Islay, a significant increase in crude adult annual survival rate (based on census data) occurred after the hunting ban. Numbers on Islay continue to show linear increase. At Wexford, there was no significant difference between crude adult survival before and after the hunting ban where, after a short period of increase, numbers stabilised at 8,000–10,000 after 1990. There were no significant differences in the proportions of young birds before and after protection in these two flocks. Despite overall population increase, seven flocks have become extinct during 1982–1995 and a further five are close to extinction. Eighteen flocks have declined since protection, 35 showed no significant trends and 20 showed increases. Multivariate analysis suggests size, number and quality of feeding areas, levels of disturbance, flock size and latitude influence flock status ‐ smallest most southerly flocks on fewest, poor quality limited feeding ranges showing most serious declines. The consequences of increasing concentration of the population at a few wintering areas need urgent attention and mechanisms should be sought to maintain current ...