|Scientific Name:||Anser brachyrhynchus Baillon, 1834|
|Taxonomic Source(s):||Cramp, S. and Simmons, K.E.L. (eds). 1977-1994. Handbook of the birds of Europe, the Middle East and Africa. The birds of the western Palearctic. Oxford University Press, Oxford.|
|Red List Category & Criteria:||Least Concern ver 3.1|
|Reviewer(s):||Butchart, S. & Symes, A.|
|Facilitator/Compiler(s):||Ekstrom, J., Butchart, S., Malpas, L. & Ashpole, J|
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.
|Previously published Red List assessments:|
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 (Central Asian Russia, European Russia); Slovakia; Slovenia; Spain (Canary Is.); Switzerland; United States
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||The global population is estimated at c. 410,000 individuals (Wetlands International 2015). The European population is estimated at 57,000-74,000 pairs, which equates to 114,000-148,000 mature individuals (BirdLife International 2015).|
Trend Justification: The overall trend is suspected to be increasing (Wetlands International 2015). In Europe the population size is estimated to be increasing (BirdLife International 2015).
|Current Population Trend:||Increasing|
|Habitat and Ecology:||Behaviour This species is fully migratory (del Hoyo et al. 1992), travelling on a narrow front (Kear 2005a) between separate breeding and wintering grounds (del Hoyo et al. 1992). It breeds from mid-May to late-June or early-July (Kear 2005a) in territorial pairs (Madge and Burn 1988) which may form loose colonies (Madge and Burn 1988, del Hoyo et al. 1992) of not more than c.10 pairs (Snow and Perrins 1998). After breeding the species undergoes a flightless moulting period in July and August that lasts for c.25 days (Scott and Rose 1996), during which it remains close to open water (such as the sea or early thawing lakes) (Kear 2005a). Icelandic non-breeding flocks migrate to staging areas (Madge and Burn 1988, Kear 2005a) in east Greenland to moult, whereas breeding birds from Svalbard, Greenland and Iceland remain near their breeding areas (Scott and Rose 1996). After moulting the species departs from its breeding and staging grounds (Kear 2005a) from August to mid-September (Madge and Burn 1988), most arriving on the wintering grounds in October (Madge and Burn 1988). Outside of the breeding season the species remains highly gregarious (Madge and Burn 1988), generally forming large concentrations in the autumn (commonly up to 5,000 in the UK) (Snow and Perrins 1998) and in winter (Madge and Burn 1988). These aggregations are usually loose however, with large roosting flocks dispersing into smaller foraging groups by day (Snow and Perrins 1998). During the winter the species roosts on water by night and forages in nearly all hours of daylight (Kear 2005a). Habitat Breeding The species breeds on rocky outcrops, crags, steep river gorges (del Hoyo et al. 1992, Kear 2005a), cliffs, riverbanks and snow-free hummocks near areas of lush vegetation (Greenland) (Kear 2005a) in open arctic tundra (del Hoyo et al. 1992), especially near seabird colonies (Kear 2005a). 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 lakes (Kear 2005a). Non-breeding The species overwinters on extensive areas of saltmarsh (Madge and Burn 1988, Kear 2005a) in estuaries (del Hoyo et al. 1992) and on flat agricultural land (del Hoyo et al. 1992) (e.g. improved or fertilised grasslands, stubble fields, pastures and newly sown cereal fields) (Kear 2005a). In Scotland favoured winter daytime roosting sites include estuarine mudflats, lochs and reservoirs (Madge and Burn 1988). Diet The species is hebivorous (del Hoyo et al. 1992) and an opportunistic forager (Kear 2005a). Breeding During the breeding season its diet consists of the leaves, stems, roots, berries and seed-heads of sedges, mosses, lichens (del Hoyo et al. 1992), Empetrum spp. and grasses (Kear 2005a). Non-breeding In its wintering areas the species is more reliant on grass, grain, vegetables (e.g. carrots, sugar beet (Kear 2005a)) and potatoes grown on agricultural land (del Hoyo et al. 1992). Breeding site The nest is a low mound of vegetation (del Hoyo et al. 1992, Kear 2005a) on cliffs, rocky outcrops or snow-free hummocks (Kear 2005a) often near seabird colonies (Kear 2005a). The species nests in territorial pairs (Madge and Burn 1988) which may from loose colonies (Madge and Burn 1988, del Hoyo et al. 1992) of not more than c.10 pairs, with neighbouring nests spaced as little as 5 m apart (usually more than 75 m apart) (Snow and Perrins 1998). 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) (Vickery and Gill 1999). 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) (Vickery and Gill 1999). 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) (Larsen and Madsen 2000).|
|Systems:||Terrestrial; Freshwater; Marine|
|Continuing decline in area, extent and/or quality of habitat:||Unknown|
|Generation Length (years):||11.4|
|Movement patterns:||Full Migrant|
|Congregatory:||Congregatory (and dispersive)|
|Major Threat(s):||The species is hunted illegally in the spring in Iceland which may become a threat (Kear 2005a). 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) (Kear 2005a). Disturbance from farmers discouraging foraging individuals from their land in the winter has been shown to reduce the species's reproductive success in the spring (Madsen 1995), and the species is also threatened by general disturbance (e.g. from helicopters surveying areas for oil exploration) (Mosbech and Glahder 1991). It may be threatened by land-management changes (such as a reduction in the intensity of management and land abandonment) (Tombre et al. 2005), and by future habitat loss such as the development of hydroelectric projects on interior rivers in Iceland (which would flood a major moulting area) (Kear 2005a). The nesting success of breeding pairs in Svalbard is greatly reduced as a result of arctic fox Vulpes lagopus predation (Madsen et al. 1992). 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 sizes (O'Connell et al. 2006).|
Conservation Actions Underway
EU Birds Directive Annex II. CMS Appendix II. In the Netherlands and the UK and some other areas in Europe, governments compensate farmers in relevant goose areas to support conservation. Recent population increases are most likely due to the protection of sites, changed behaviour (birds using inland roosting sites such as reservoirs), improved food supplies and a reduction of hunting. Although the species is considered legitimate quarry in all European range states, special restrictions are in force throughout, for example in Denmark goose shooting is only permitted in the early morning during a short autumn season and recreational hunting in spring is banned everywhere (Carboneras and Kirwan 2014). In 2012 an International Species Management Plan was developed for the Svalbard population (Madsen and Williams 2012).
Conservation Actions Proposed
The following proposed actions refer to the species's European range only: Compensation schemes for farmers should be continued and improved. Research in Norway has suggested the current compensation scheme can be made ten times more efficient through strategic prioritization. Careful management in important areas is needed to maintain the current population. In the UK, one study suggested that the manipulation of sward height and fertiliser application provides suitable habitat for this and other species of geese (Carboneras and Kirwan 2014). Hunting should be monitored and sustainable hunting levels ensured where hunting is in practice. Spatial management should be enhanced and maintained (Madsen and Williams 2012).
|Citation:||BirdLife International. 2016. Anser brachyrhynchus. The IUCN Red List of Threatened Species 2016: e.T22679872A85978254.Downloaded on 19 March 2018.|
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