|Scientific Name:||Branta ruficollis|
|Species Authority:||(Pallas, 1769)|
|Taxonomic Source(s):||del Hoyo, J., Collar, N.J., Christie, D.A., Elliott, A. and Fishpool, L.D.C. 2014. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Lynx Edicions BirdLife International.|
|Identification information:||53-56 cm. Unmistakable red, black and white goose. Chestnut-red foreneck, breast and sides of head, bordered white. White flank-stripe and black belly. White rear belly and black tail. Juvenile generally duller than adult. Short neck and dark belly stand out in flight. Similar spp. Can be surprisingly difficult to detect amongst large flocks of other geese. Voice Repeated, jerky kik-yoik, kik-yik in flight.|
|Red List Category & Criteria:||Vulnerable A2bcd+3bcd+4bcd ver 3.1|
|Contributor(s):||Bukreev, S., Dereliev, S., Hulea, D., Mikityuk, A., Petkov, N., Zöckler, C., Rozenfeld, S., Simeonov, Cranswick, P., Todorov, E., Nagy, S., Choudhury, U., Mooij, J. & Zalai, T.|
|Facilitator/Compiler(s):||Benstead, P., Bird, J., Butchart, S., Capper, D., Derhé, M., Harding, M., Peet, N., Pilgrim, J., Pople, R. & Ashpole, J|
This species has a moderately small population which appears to be declining over a short time period. The reasons for this decline are largely unknown. Trend calculations are complicated by interannual variation in survey coverage and reporting across its range. Small populations of other Arctic breeding geese have shown dramatic population fluctuations and this may prove to be the case for this species. The species is precautionarily listed as Vulnerable, however if it is found that recent increases are genuine and not a result of improved monitoring efforts or range shifts the species may warrant further downlisting.
|Previously published Red List assessments:||
|Range Description:||This species breeds on the Taimyr (70% of the population), Gydan and Yamal peninsulas, Russia (Hunter and Black 1996). In winter, prior to the 1950s, much of the population occurred along the western coast of the Caspian Sea, mainly in Azerbaijan, and in Iran and Iraq. The wintering area then rapidly shifted to the western Black Sea coast, and 80-90% of birds now congregate in January/ February at 5-10 roost sites on the Black Sea coast, particularly at Shabla Lakes and Durankulak Lake, Bulgaria, Razelm-Sinoe lagoons, Romania, and in the coastal area between the rivers Danube and Dniester in Ukraine (A. Mikityuk in litt. 1999, Rusev et al. 2008, Cranswick et al. 2010). Small numbers also winter in Azerbaijan. The precise distribution in winter varies according to the severity of the weather from the Crimean peninsula to the Dobrudzha region of Bulgaria. In cold weather, small numbers are occasionally on the Aegean shore of Greece and Turkey (Cranswick et al. 2010); during prolonged mild periods, significant numbers may remain in Kalmykya, Stavropol and Rostov districts in Russia (S. Rozenfeld in litt. 2012). Migration is believed to follow a relatively narrow route south down the Ob to Kazakhstan (though a small number of ringing recoveries point to some birds passing to the west of the Urals) and then east to the Black Sea. There are four known main staging areas: the Lower Ob, Middle Ob and Kumo-Manych depression in Russia, and the Northern and Kostanay regions of Kazakhstan. They are also regularly recorded in small numbers on passage in Hungary (e.g. Pigniczki 2008). There may be other, currently unknown, staging sites and knowledge of the migration route, particularly in Siberia, should therefore be considered incomplete. It is also possible that some wintering grounds remain undetected (perhaps in eastern Ukraine and southwest Russia), and use of these areas during mild weather may account for the variation in winter survey totals in recent years.
Maximum population counts from wintering or staging areas were 60,000 between 1967-1970, 25,907 between 1976-1990, 75,879 between 1991-1995, 88,000 in 1996 (Aarvak et al. 1996), 60,444 between 1998-2001 (with a maximum of 88,425 in winter 2000) (D. Hulea in litt. 2003) and 56,860 in 2010 (Rozenfeld 2011a). It is unclear whether these represent genuine population fluctuations or are due to incomplete surveying of the species following suspected alteration its winter distribution (as has been seen in the late 1960s following deterioration of wintering conditions in Azerbaijan) with larger numbers of birds now short-stopping and over-wintering in Ukraine (Rusev et al. 2008, Cranswick et al. 2010) and in areas in Romania (N. Petkov in litt.), where monitoring is more difficult and less comprehensive. Coordinated censuses in January 2003, 2004, 2005 and 2006 resulted in totals of 33,600, 52,800, 32,100 and c.34,000 respectively, with a mean population estimate of 37,300 (S. Dereliev in litt. to Wetlands International 2005). Total counts recorded 40,800 individuals in spring 2008 and 44,300 in 2009 (Cranswick et al. 2010). In 2015, Wetlands International increased its global population estimate from c.44,000 to c.56,000 individuals (Wetlands International 2015).
Native:Armenia (Armenia); Austria; Bulgaria; Croatia; Greece; Iran, Islamic Republic of; Iraq; Kazakhstan; Macedonia, the former Yugoslav Republic of; Moldova; Montenegro; Romania; Russian Federation; Serbia (Serbia); Turkey; Ukraine
Vagrant:Azerbaijan; Belarus; Belgium; Bosnia and Herzegovina; China; Cyprus; Denmark; Egypt; Finland; France; Georgia; Germany; Greenland; Hungary; India; Ireland; Israel; Italy; Latvia; Netherlands; Norway; Poland; Slovakia; Spain; Svalbard and Jan Mayen; Sweden; United Kingdom
Present - origin uncertain:Afghanistan; Kyrgyzstan; Syrian Arab Republic; Tajikistan; Turkmenistan; Uzbekistan
|Continuing decline in area of occupancy (AOO):||No|
|Extreme fluctuations in area of occupancy (AOO):||No|
|Estimated extent of occurrence (EOO) - km2:||44200|
|Continuing decline in extent of occurrence (EOO):||No|
|Extreme fluctuations in extent of occurrence (EOO):||No|
|Number of Locations:||6-10|
|Continuing decline in number of locations:||No|
|Extreme fluctuations in the number of locations:||No|
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||Coordinated censuses in January 2003, 2004 and 2005 resulted in total population estimates of 33,600, 52,800 and 32,100 individuals respectively. The geometric mean of these totals 38,500. Recalculating this including the 2006 count of c.34,000 gives a revised geometric mean of 37,000 individuals. However, total counts of 40,800 in spring 2008 (primarily as a result of a large count in Kalmykia), 44,300 the following winter (Cranswick et al. 2010) and a maximum population count of 56,860 in autumn 2010 (Rozenfeld 2011a) lend further weight to the suggestion that counts in the mid 2000s might be partially incomplete because birds wintered away from the traditionally surveyed sites. In 2015, Wetlands International increased its global population estimate from c. 44,000 to c. 56,000 individuals (Wetlands International 2015).
Variation in survey intensity and coverage historically makes determination of trends difficult. Following a count of 60,000 in the mid 1950s, totals rarely exceeded 20,000 until intensive winter surveys in the 1990s recorded over 70,000. Two counts of just under 90,000 in the late 1990s were considered accurate (Aarvak et al. 1996, D. Hulea in litt. 2003) and an increase since the 1970s. Coordinated winter counts were then initiated in Bulgaria, Romania and Ukraine since 1995, with at least one count in each winter month. Only around 30,000 were recorded in the early 2000s. It has been suggested that some birds may have been overlooked, wintering further east than expected (in eastern Ukraine or south-west Russia) where survey coverage was much less comprehensive or absent, though no new wintering sites have been found. Numbers recorded during winter surveys recovered slightly, with an average of 37,300 during the mid 2000s (S. Dereliev in litt. to Wetlands International 2005), but representing a decline of more than 50% since the late 1990s.
|Current Population Trend:||Decreasing|
|Habitat and Ecology:||It breeds in tundra or scrubby 'wooded' tundra (Madge and Burn 1988, del Hoyo et al. 1992), in close proximity to rivers and gulleys (Madge and Burn 1988). It favours high and dry areas on steep river banks and precipices, low hills, rock outcrops and rocky islands (Kear 2005). Less commonly it inhabits low islands in lowland areas (Kear 2005). Vegetative cover in its preferred habitats is usually thin and includes dwarf birch Betula, willow Salix, and dead grass (Kear 2005). During the non-breeding season it inhabits open steppe and open rolling lowland hills, feeding among steppe, coastal lines, pasture, stubble and crop fields (Madge and Burn 1988). Throughout the day it flies to coastal and freshwater lakes to drink (Kear 2005). Occasionally it also roosts at these lakes, using the middle of the water or remote shallow areas and muddy and sandy beaches with low aquatic vegetation (Kear 2005). It will also roost on frozen lakes or on the sea (Kear 2005). The distribution of geese from year to year depends a lot on differences in lake water levels. On its breeding grounds it feeds primarily on Fabaceae and to a lesser extent grass leaves and the shoots of cotton-grasses Eriophorum angustifolium and E. scheuchzeri (Rosenfeld and Volkov 2001), as well as some Carex and Equisetum spp. (Kear 2005). Wintering geese feed on winter wheat, barley, maize, pasture and steppe grasses and, in Greece, natural grassland (Kear 2005). In Kazakhstan on passage they feed mainly on spilled grain on the fields after harvesting the wheat crops in autumn. They also feed on arid-adapted herbs such as Salicornia (Johnsgard 1978). At migration staging areas the diet is thought to consist largely of grass shoots, supplemented with tubers and rhizomes (Kear 2005), whilst at the Kumo-Manych stopover site, the diet consists of the salt marsh’s galophyte complex of Puccinellia distans and Aeroplus littoralis (Rozenfeld 2011b).
The species nests in hollows and fissures in the ground, usually 50-80 mm deep and 200 mm in diameter (Kear 2005). They are often constructed near to the eyries of birds of prey (Kear 2005), since breeding success may depend on nesting Peregrine Falcon Falco peregrinus, Snowy Owl Bubo scandiaca and Rough-legged Buzzard Buteo lagopus providing protection from predators (Quinn et al. 1996, Prop and Quinn 2003, Quinn et al. 2003, S. Rozenfeld in litt. 2012). Successful breeding seasons are also associated with good lemming years, and it has been suggested that this may be because predators are sated by the lemming population and so predation of geese is much lower.
This species is highly migratory (del Hoyo et al. 1992). Following the post-breeding moult it migrates southwards over land in mid- to late-September (del Hoyo et al. 1992, Kear 2005), arriving on its wintering grounds in October-November. Here it is highly gregarious and occurs in flocks, regularly in association with the White-fronted Goose Anser albifrons (Madge and Burn 1988) Lesser White-fronted Goose A. erythropus and Greylag Goose A. anser. The return journey is made between March and May (del Hoyo et al. 1992), often together with A. albifrons (Kear 2005). It flies in dense flocks rather than in the defined V-formation typical of other goose species (Kear 2005), and arrives on its breeding grounds in small flocks of 3-15 individuals (Johnsgard 1978). It begins to breed in June in loose colonies, usually of around five to fifteen pairs (Madge and Burn 1988, del Hoyo et al. 1992, S. Rozenfeld in litt. 2012), although up to 37 have been observed (Kear 2005).
|Systems:||Terrestrial; Freshwater; Marine|
|Continuing decline in area, extent and/or quality of habitat:||Yes|
|Generation Length (years):||10.9|
|Movement patterns:||Full Migrant|
|Congregatory:||Congregatory (and dispersive)|
Deliberate hunting of birds occurs in Russia and Kazakhstan (Rozenfeld 2009, 2011b), and results from a recent tagging study suggest mortality owing to hunting could be very high (N. Petkov in litt. 2015). Following land privatization, and especially the residential and tourist development boom in winter roosting and feeding areas, the quality of roosting areas has decreased. In addition, the low profitability of agriculture has reduced the area under winter wheat cultivation which, together with conversion to other crops, has decreased the availability of food. Some key feeding sites have been lost in Bulgaria (S. Dereliev in litt. 1999). Hunting pressure on waterfowl as a whole is also substantial in Bulgaria and Romania, including illegal shooting at Red-breasted Goose (Simeonov in litt. 2007, E. Todorov in litt. 2015). There are no effective hunting-free areas around roost sites in Bulgaria (hunting is only prohibited for 100m around the lake edge, and this rule is regularly ignored). However, conservation activities in the area of Shabla and Durankulak lakes have reduced deliberate shooting of the species in 2010-2012 (N. Petkov in litt. 2012). Disturbance in the lakes used for roosts is also caused by poachers and fishermen (Dereliev 1997, D. Hulea in litt. 2006, Dereliev and Georgiev, 2002). Disturbance/chasing of feeding birds by hunters (because they associate with White-fronted Geese Anser erythropus, a legal quarry species) is a significant limitation on foraging behaviour and prenuptial accumulation of fat reserves, which has a negative effect on survival during spring migration and breeding (N. Petkov in litt. 2007). Hunting by tourists in Ukraine poses an increasing threat (WWT TWSG News 10 1997) and birds are shot at staging grounds in Russia.
Climate change and associated habitat shifts are expected to impact negatively on this species and others dependent on tundra habitat for breeding. Modelling indicates that 67% of the habitat for this species could be lost by 2070 (Zöckler and Lysenko 2000). The increase in oil and gas operations in the region has seen a significant expansion into previously remote areas and has resulted in disturbance of breeding birds as well as direct habitat loss to a small degree. Further expansion of operations in the region is anticipated (Cranswick et al. 2010). Other threats include industrial developments at breeding sites in Gydan and Yamal, the use of rodenticides in the wintering grounds, as well as displacement by windfarms in the wintering areas. A major recent threat is the expansion in windfarms in the wintering areas since 2008. Many thousands of wind turbines have been proposed in Dobrudhza area both in Bulgaria and Romania, including large complexes adjacent to IBAs and SPAs. Data analysis from wintering grounds in Bulgaria suggest that there is already impact of the constructed windfarms leading to displacement and shifting of the foraging areas (Petkov et al. 2012).
Conservation and Research Actions Underway
CITES Appendix II. CMS Appendix I and II. It is legally protected in key states (Hunter et al. 1999). It is listed in the (national and regional) Red Book of Russia and Red Books of Kazakhstan and Bulgaria. Parts of its breeding range and principal wintering roost sites are protected (some qualifying as Ramsar sites), including the implementation of hunting regulations and hunting-free areas in Russia and Kazakhstan, although hunting occurs in many feeding areas. A management plan is being implemented for roosting lakes in Bulgaria (S. Dereliev in litt. 1999). Wintering sites in Bulgaria and Romania are monitored and research and public awareness projects are ongoing (S. Dereliev in litt. 1999, D. Hulea in litt. 1999, Hunter et al. 1999). An International action plan was published in 2010 (Cranswick et al. 2010). An International Species Working Group is active and a coordinator is in place. In 2010 an EU Life project began in Bulgaria, which aims to address many of the key threats operating on the wintering grounds. A study of geese distribution, movements and feeding preferences will enable a sensitivity map to be developed and goose-sensitive guidance provided to authorities to help guide development proposals. A Life-funded project was carried out in Romania in 2005-2008 with the aim of improving the habitat quality of an important saltwater lake used by the species and developing a National Action Plan for the species (Raducescu 2013). A payment for the species has been included in the National agri-environmental programme of Romania. In Bulgaria, an agri-environmental payment for farmers for seeding winter wheat in key wintering areas for geese was introduced in 2012. Spring-hunting of wildfowl was prohibited in southwest Russia in spring 2012.
Conservation and Research Actions Proposed
Study migration patterns and determine species's non-breeding range using satellite telemetry. Expand monitoring and research programmes, especially in Ukraine and Romania to determine whether more birds are overwintering there. Implement a Strategy for Hunting and Waterbird Resource Management (Rozenfeld 2011b). Regulate hunting in key sites (particularly spring hunting in Russia and Kazakhstan). Monitor and reduce disturbance and illegal hunting. Monitor breeding population in Russia to determine population trends. Identify and protect key staging areas. Prevent loss of roosting lakes to urbanization. Monitor changes in agriculture and propose measures (in EU agri-environmental measures ) to ensure suitable foraging habitat is available. Promote beneficial agricultural policies and spatial crop rotation planning around roosting areas. Continue public awareness initiatives. Lobby for full designation of qualifying wetlands and feeding areas as Natura 2000 sites, ensure hunting is not allowed within them and ensure they are properly managed.
|Citation:||BirdLife International. 2015. Branta ruficollis. The IUCN Red List of Threatened Species 2015: e.T22679954A84085554. . Downloaded on 24 May 2016.|
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