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Anser brachyrhynchus

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Taxonomy [top]

Kingdom Phylum Class Order Family
ANIMALIA CHORDATA AVES ANSERIFORMES ANATIDAE

Scientific Name: Anser brachyrhynchus
Species Authority: Baillon, 1834
Common Name/s:
English Pink-footed Goose

Assessment Information [top]

Red List Category & Criteria: Least Concern     ver 3.1
Year Published: 2009
Assessor/s: BirdLife International
Reviewer/s: Bird, J., Butchart, S.
Justification:
This species has a very large range, and hence does not approach the thresholds for Vulnerable under the range size criterion (Extent of Occurrence <20,000 km2 combined with a declining or fluctuating range size, habitat extent/quality, or population size and a small number of locations or severe fragmentation). The population trend appears to be increasing, and hence the species does not approach the thresholds for Vulnerable under the population trend criterion (>30% decline over ten years or three generations). The population size is very large, and hence does not approach the thresholds for Vulnerable under the population size criterion (<10,000 mature individuals with a continuing decline estimated to be >10% in ten years or three generations, or with a specified population structure). For these reasons the species is evaluated as Least Concern.
History:
2008 Least Concern
2004 Least Concern

Geographic Range [top]

Countries:
Native:
Belgium; Czech Republic; Denmark; Finland; France; Germany; Greenland; Iceland; Ireland; Netherlands; Norway; Romania; Svalbard and Jan Mayen; Sweden; United Kingdom
Vagrant:
Austria; Canada; Hungary; Italy; Luxembourg; Poland; Portugal; Russian Federation; Russian Federation; Slovakia; Slovenia; Spain; Switzerland; United States
Range Map: Click here to open the map viewer and explore range.

Habitat and Ecology [top]

Habitat and Ecology: Behaviour This species is fully migratory1, travelling on a narrow front2 between separate breeding and wintering grounds1. It breeds from mid-May to late-June or early-July2 in territorial pairs3 which may form loose colonies1, 3 of not more than c.10 pairs5. After breeding the species undergoes a flightless moulting period in July and August that lasts for c.25 days4, during which it remains close to open water (such as the sea or early thawing lakes)2. Icelandic non-breeding flocks migrate to staging areas2, 3 in east Greenland to moult, whereas breeding birds from Svalbard, Greenland and Iceland remain near their breeding areas4. After moulting the species departs from its breeding and staging grounds2 from August to mid-September3, most arriving on the wintering grounds in October3. Outside of the breeding season the species remains highly gregarious3, generally forming large concentrations in the autumn (commonly up to 5,000 in the UK)5 and in winter3. These aggregations are usually loose however, with large roosting flocks dispersing into smaller foraging groups by day5. During the winter the species roosts on water by night and forages in nearly all hours of daylight2. Habitat Breeding The species breeds on rocky outcrops, crags, steep river gorges1, 2, cliffs, riverbanks and snow-free hummocks near areas of lush vegetation (Greenland)2 in open arctic tundra1, especially near seabird colonies2. Later in the summer the species forages chiefly on damp sedge-meadows, and while moulting and flightless it remains close to the sea or early-thawing lakes2. Non-breeding The species overwinters on extensive areas of saltmarsh2, 3 in estuaries1 and on flat agricultural land1 (e.g. improved or fertilised grasslands, stubble fields, pastures and newly sown cereal fields)2. In Scotland favoured winter daytime roosting sites include estuarine mudflats, lochs and reservoirs3. Diet The species is hebivorous1 and an opportunistic forager2. Breeding During the breeding season its diet consists of the leaves, stems, roots, berries and seed-heads of sedges, mosses, lichens1, Empetrum spp. and grasses2. Non-breeding In its wintering areas the species is more reliant on grass, grain, vegetables (e.g. carrots, sugar beet2) and potatoes grown on agricultural land1. Breeding site The nest is a low mound of vegetation1, 2 on cliffs, rocky outcrops or snow-free hummocks2 often near seabird colonies2. The species nests in territorial pairs3 which may from loose colonies1, 3 of not more than c.10 pairs, with neighbouring nests spaced as little as 5 m apart (usually more than 75 m apart)5. Management information An investigation carried out in one of the species's wintering areas (UK) found that it was most likely to forage on grasslands a minimum of 6 ha in area, managed by livestock grazing or mechanical cutting, with an optimum sward height of 13-20 cm (although the species was also found to use heavily grazed land down to a sward height to 1.5 cm), at a distance of less than 10 km away from roosting sites (the optimum distance was 2-5 km away)7. Fertilising the grassland with nitrogenous fertiliser (ammonium nitrate 34.5 % N) in early-March at a rate of 80 kg N ha1 was also found to double the grazing intensity of geese compared to unfertilised areas (although no further increases were found with higher rates of fertiliser application)7. Studies in the Vejlerne nature reserve, Denmark found that wind turbines placed in lines or small clusters cause less disturbance to the species than large clusters (small clusters may be placed in conjunction with existing physical elements such as roads, wind-breaks or buildings, and are therefore less likely to coincide with grasslands areas used for grazing by the species)8.

Systems: Terrestrial; Freshwater; Marine

Threats [top]

Major Threat(s): The species is hunted illegally in the spring in Iceland which may become a threat2. Disturbance from hunting on spring staging grounds in Norway has major negative impact on breeding success, and persecution (shooting and disturbance) of the species by farmers is likely to increase in the future if populations increase (due to the species's impact on agricultural grassland)2. Disturbance from farmers discouraging foraging individuals from their land in the winter has been shown to reduce the species's reproductive success in the spring11, and the species is also threatened by general disturbance (e.g. from helicopters surveying areas for oil exploration)10. It may be threatened by land-management changes (such as a reduction in the intensity of management and land abandonment)9, and by future habitat loss such as the development of hydroelectric projects on interior rivers in Iceland (which would flood a major moulting area)2. The nesting success of breeding pairs in Svalbard is greatly reduced as a result of arctic fox Vulpes lagopus predation12. Utilisation The species is subject to hunting in Svalbard, Norway and Denmark, although mortality due to hunting does not seem to be a major factor controlling population sizes6.

Citation: BirdLife International 2009. Anser brachyrhynchus. In: IUCN 2011. IUCN Red List of Threatened Species. Version 2011.2. <www.iucnredlist.org>. Downloaded on 24 May 2012.
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