Anser fabalis

Taxonomy

Assessment Information

Geographic Range

Population

Habitat and Ecology

Threats

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Taxonomy [top]

Kingdom	Phylum	Class	Order	Family
ANIMALIA	CHORDATA	AVES	ANSERIFORMES	ANATIDAE

Scientific Name:

Anser fabalis

Species Authority:

(Latham, 1787)

Common Name/s:

English	–	Bean Goose
French	–	Oie des moissons

Taxonomic Notes:

Anser fabalis (Sibley and Monroe 1990, 1993) has been split into A. fabalis and A. serrirostris by Sangster and Oreel (1996) and A. fabalis and A. middendorfi by Ruokonen et al. (2008). Given that these two treatments are contradictory and undermine one another's evidence we reject both treatments and retain one polyphyletic species A. fabalis.

Assessment Information [top]

Red List Category & Criteria:

Least Concern ver 3.1

Year Published:

2012

Assessor/s:

BirdLife International

Reviewer/s:

Butchart, S. & Symes, A.

Contributor/s:

Justification:
This species has an extremely 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). Despite the fact that the population trend appears to be decreasing, the decline is not believed to be sufficiently rapid to 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:

2009	–	Least Concern
2008	–	Least Concern
2004	–	Least Concern

Geographic Range [top]

Countries:	Native: Albania; Austria; Belarus; Belgium; Bosnia and Herzegovina; Bulgaria; Canada; China; Croatia; Czech Republic; Denmark; Finland; France; Germany; Greece; Hungary; Iran, Islamic Republic of; Italy; Japan; Kazakhstan; Korea, Democratic People's Republic of; Korea, Republic of; Latvia; Liechtenstein; Lithuania; Luxembourg; Macedonia, the former Yugoslav Republic of; Mexico; Mongolia; Montenegro; Netherlands; Norway; Poland; Romania; Russian Federation; Russian Federation; Russian Federation; Serbia (Serbia); Slovakia; Slovenia; Spain; Sweden; Switzerland; Taiwan, Province of China; Tajikistan; Turkey; Ukraine; United Kingdom; Uzbekistan Vagrant: Algeria; Bangladesh; Egypt; Hong Kong; Iceland; India; Ireland; Kyrgyzstan; Lebanon; Mali; Malta; Morocco; Myanmar; Nepal; Portugal; United States
Range Map:	Click here to open the map viewer and explore range.

Countries:

Native:

Albania; Austria; Belarus; Belgium; Bosnia and Herzegovina; Bulgaria; Canada; China; Croatia; Czech Republic; Denmark; Finland; France; Germany; Greece; Hungary; Iran, Islamic Republic of; Italy; Japan; Kazakhstan; Korea, Democratic People's Republic of; Korea, Republic of; Latvia; Liechtenstein; Lithuania; Luxembourg; Macedonia, the former Yugoslav Republic of; Mexico; Mongolia; Montenegro; Netherlands; Norway; Poland; Romania; Russian Federation; Russian Federation; Russian Federation; Serbia (Serbia); Slovakia; Slovenia; Spain; Sweden; Switzerland; Taiwan, Province of China; Tajikistan; Turkey; Ukraine; United Kingdom; Uzbekistan

Vagrant:

Algeria; Bangladesh; Egypt; Hong Kong; Iceland; India; Ireland; Kyrgyzstan; Lebanon; Mali; Malta; Morocco; Myanmar; Nepal; Portugal; United States

Range Map:

Click here to open the map viewer and explore range.

Population [top]

Population Trend:	Decreasing

Population Trend:

Decreasing

Habitat and Ecology [top]

Habitat and Ecology:	Behaviour This species is strongly migratory and travels between breeding grounds in the high Arctic to wintering grounds in the temperate and subtropical zones (del Hoyo et al. 1992). Populations that breed in the taiga nest in early-May, with those breeding in the tundra nesting one month later in early-June (del Hoyo et al. 1992, Kear 2005a). The species breeds in solitary pairs, usually with nests well-dispersed (Snow and Perrins 1998) (although it will also nest in loose groups) (del Hoyo et al. 1992). After breeding the species undergoes a moulting period when it is flightless for c.1 month between July and August (Scott and Rose 1996), some populations undertaking extensive northward moult migrations (Kear 2005a), and most congregating into large moulting flocks near open water (Scott and Rose 1996). The species departs from its breeding grounds after this post-breeding moulting period in early-September, arriving in the winter quarters from late-September through October (Madge and Burn 1988). It remains gregarious throughout the winter (Madge and Burn 1988) (although it occurs in smaller, loose flocks than many other goose species) (Snow and Perrins 1998) and roosts close to feeding areas (Madge and Burn 1988) in mixed-species flocks on lakes, rivers and flooded lands (Kear 2005a). Habitat Breeding The species breeds near lakes, pools, rivers and streams in high Arctic tundra or the taiga forest zone (del Hoyo et al. 1992). Taiga nesting populations show a preference for scrubby birch Betula spp. forest (Madge and Burn 1988) and dense spruce forest with bogs or mires (Madge and Burn 1988), whereas tundra-based populations nest on damp tundra of moss, grass, sedge or scrub (Johnsgard 1978) near river flood-plains (but above flood levels) (Madge and Burn 1988, Kear 2005a), on Arctic islands and in Arctic coastal regions (Madge and Burn 1988). Non-breeding During the winter and on passage the species inhabits marshes, agricultural land (del Hoyo et al. 1992) (pastures, arable fields, rice-paddies) (Kear 2005a), damp steppe grassland (Madge and Burn 1988), flood-lands, rivers and coastal shallows (Snow and Perrins 1998) in open country (del Hoyo et al. 1992). It also roosts on lakes, rivers and flood-lands in Europe during this season (Kear 2005a). Diet The species is herbivorous (del Hoyo et al. 1992), its diet consisting of herbs, grasses, sedges (del Hoyo et al. 1992) and mosses (Johnsgard 1978), complemented during the breeding season by berries (e.g. from Empetrum or Vaccinium spp.) (del Hoyo et al. 1992). During the winter it feeds predominantly on agricultural land taking grain, beans, potatoes (del Hoyo et al. 1992) and sprouting winter cereal crops (Kear 2005a). Breeding site The species builds a nest of vegetation in a shallow scrape on the ground (del Hoyo et al. 1992). Taiga breeders nest in bogs or mires within forested regions, placing nests within 400 m of open mire and within 2 km of open water, usually 50-100 cm above bog surfaces on hummocks that are safe from flooding (Kear 2005a). Tundra breeders nest on dry hummocks and moss (Kear 2005a). Management information An investigation carried out in one of the species' wintering areas (UK) found that it was most likely to forage on improved grassland or grasslands grazed by cattle that were a minimum of 5 ha in area, had an optimum sward height of c.20 cm and were at a distance of less than 9 km away from roosting sites (Vickery and Gill 1999).
Systems:	Terrestrial; Freshwater

Habitat and Ecology:

Behaviour This species is strongly migratory and travels between breeding grounds in the high Arctic to wintering grounds in the temperate and subtropical zones (del Hoyo et al. 1992). Populations that breed in the taiga nest in early-May, with those breeding in the tundra nesting one month later in early-June (del Hoyo et al. 1992, Kear 2005a). The species breeds in solitary pairs, usually with nests well-dispersed (Snow and Perrins 1998) (although it will also nest in loose groups) (del Hoyo et al. 1992). After breeding the species undergoes a moulting period when it is flightless for c.1 month between July and August (Scott and Rose 1996), some populations undertaking extensive northward moult migrations (Kear 2005a), and most congregating into large moulting flocks near open water (Scott and Rose 1996). The species departs from its breeding grounds after this post-breeding moulting period in early-September, arriving in the winter quarters from late-September through October (Madge and Burn 1988). It remains gregarious throughout the winter (Madge and Burn 1988) (although it occurs in smaller, loose flocks than many other goose species) (Snow and Perrins 1998) and roosts close to feeding areas (Madge and Burn 1988) in mixed-species flocks on lakes, rivers and flooded lands (Kear 2005a). Habitat Breeding The species breeds near lakes, pools, rivers and streams in high Arctic tundra or the taiga forest zone (del Hoyo et al. 1992). Taiga nesting populations show a preference for scrubby birch Betula spp. forest (Madge and Burn 1988) and dense spruce forest with bogs or mires (Madge and Burn 1988), whereas tundra-based populations nest on damp tundra of moss, grass, sedge or scrub (Johnsgard 1978) near river flood-plains (but above flood levels) (Madge and Burn 1988, Kear 2005a), on Arctic islands and in Arctic coastal regions (Madge and Burn 1988). Non-breeding During the winter and on passage the species inhabits marshes, agricultural land (del Hoyo et al. 1992) (pastures, arable fields, rice-paddies) (Kear 2005a), damp steppe grassland (Madge and Burn 1988), flood-lands, rivers and coastal shallows (Snow and Perrins 1998) in open country (del Hoyo et al. 1992). It also roosts on lakes, rivers and flood-lands in Europe during this season (Kear 2005a). Diet The species is herbivorous (del Hoyo et al. 1992), its diet consisting of herbs, grasses, sedges (del Hoyo et al. 1992) and mosses (Johnsgard 1978), complemented during the breeding season by berries (e.g. from Empetrum or Vaccinium spp.) (del Hoyo et al. 1992). During the winter it feeds predominantly on agricultural land taking grain, beans, potatoes (del Hoyo et al. 1992) and sprouting winter cereal crops (Kear 2005a). Breeding site The species builds a nest of vegetation in a shallow scrape on the ground (del Hoyo et al. 1992). Taiga breeders nest in bogs or mires within forested regions, placing nests within 400 m of open mire and within 2 km of open water, usually 50-100 cm above bog surfaces on hummocks that are safe from flooding (Kear 2005a). Tundra breeders nest on dry hummocks and moss (Kear 2005a). Management information An investigation carried out in one of the species' wintering areas (UK) found that it was most likely to forage on improved grassland or grasslands grazed by cattle that were a minimum of 5 ha in area, had an optimum sward height of c.20 cm and were at a distance of less than 9 km away from roosting sites (Vickery and Gill 1999).

Systems:

Terrestrial; Freshwater

Threats [top]

Major Threat(s):	The species declined in the past due to hunting (resulting in mortality, injury and disturbance) (del Hoyo et al. 1992, Kear 2005a, Nikolaeva et al. 2006) and habitat loss (del Hoyo et al. 1992). Habitat degradation due to oil pollution (Grishanov 2006, Nikolaeva et al. 2006), drainage, peat-extraction, changing management practices (decreased grazing and mowing in meadows leading to scrub over-growth) and forest clearance is a threat to breeding areas in Russia (Grishanov 2006), Norway and Sweden (Madge and Burn 1988). The species also suffers from human persecution (Madge and Burn 1988) and is susceptible to poisoning by pesticides used on agricultural land (Kwon et al. 2004).

Major Threat(s):

The species declined in the past due to hunting (resulting in mortality, injury and disturbance) (del Hoyo et al. 1992, Kear 2005a, Nikolaeva et al. 2006) and habitat loss (del Hoyo et al. 1992). Habitat degradation due to oil pollution (Grishanov 2006, Nikolaeva et al. 2006), drainage, peat-extraction, changing management practices (decreased grazing and mowing in meadows leading to scrub over-growth) and forest clearance is a threat to breeding areas in Russia (Grishanov 2006), Norway and Sweden (Madge and Burn 1988). The species also suffers from human persecution (Madge and Burn 1988) and is susceptible to poisoning by pesticides used on agricultural land (Kwon et al. 2004).

Citation:	BirdLife International 2012. Anser fabalis. In: IUCN 2012. IUCN Red List of Threatened Species. Version 2012.2. <www.iucnredlist.org>. Downloaded on 19 June 2013.
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