|Scientific Name:||Cepphus grylle (Linnaeus, 1758)|
|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):||Ashpole, J, Butchart, S., Calvert, R., Ekstrom, J., Hatchett, J.|
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). The population trend is unclear but it is not thought 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.
|Previously published Red List assessments:|
|Range Description:||This species can be found throughout Arctic waters on the northern coasts of Russia, Alaska (U.S.A.), Canada and Norway, in the Atlantic Ocean off Greenland (to Denmark), eastern Canada as far south as the United Kingdom including the North and Baltic Sea (del Hoyo et al. 1996).|
Native:Canada; Denmark; Estonia; Faroe Islands; Finland; Germany; Greenland; Iceland; Ireland; Latvia; Norway; Poland; Russian Federation (Central Asian Russia - Vagrant, Eastern Asian Russia, European Russia); Saint Pierre and Miquelon; Svalbard and Jan Mayen; Sweden; United Kingdom; United States
Vagrant:Belgium; Croatia; Czech Republic; France; Netherlands; Slovenia; Spain
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||The global population is conservatively estimated to number c.400,000-700,000 individuals (del Hoyo et al. 1996). However the European population alone was recently estimated at 304,000-742,000 mature individuals (BirdLife International 2015). Europe forms c.50-74% of the global range so a very preliminary estimate of the global population size is 410,000-1,484,000 mature individuals, although further validation of this estimate is needed. The population is therefore placed in the band 400,000-1,499,999 mature individuals.|
Trend Justification: The overall population trend is unclear. The population trend is increasing in North America (based on BBS/CBC data: Butcher and Niven 2007). In Europe the population size is estimated to be decreasing by less than 25% in 32.7 years (three generations) (BirdLife International 2015).
|Current Population Trend:||Unknown|
|Habitat and Ecology:||Behaviour Black Guillemots are pursuit divers that propel themselves through the water using their wings. Diet The species is probably primarily a benthic forager, since much of the prey consists of benthic fish and invertebrates, including crustaceans (Bradstreet and Brown 1985, Cairns 1987a, BirdLife International 2000). Various studies find sandeels (Ammodytes spp.) (Harris and Riddiford 1989, Ewins 1990) and blennies (particularly butterfish Pholis gunnellus) (Harris and Riddiford 1989, Ewins 1990, BirdLife International 2000) to be the most important prey species of fish, although the relative contributions of each of these to the overall diet differs. Flatfish (Harris and Riddiford 1989) and gadoids (Ewins 1990) are also sometimes important. Amongst invertebrates, sea-scorpions are noted as an important prey item (Harris and Riddiford 1989). Adults tend to consume a higher proportion of invertebrates than chicks (Ewins 1990). The general trend is for increasing importance of invertebrates with latitude (presumably reflecting overall availability) in the summer diet of both adults and chicks. The few data on winter food suggest that invertebrates are of greater importance during the winter than during the summer (Ewins 1990). Breeding site Both early spring and breeding distributions appear to be influenced by the Hell Gate and Cardigan Strait polynya located in western Jones Sound, Canada, between Ellesmere and Devon islands. The evidence presented suggests that annual variation in the distribution of ice edges in Jones Sound may influence the distribution of breeding birds among suitable breeding habitat. The observed distribution of Guillemots in March, April, and May is coincident with the location of open water and the associated ice edges. Thereafter, as the ice margin recedes and shoreleads open, the distribution of Guillemots tends to reflect the location of breeding colonies (Prach and Smith 1992). Foraging range Birds feeding in the eastern Canadian Arctic fed principally in waters 10-130 m deep (Cairns 1987a). Birds have been caught in nets up to 50 m deep, but have a theoretical maximum dive of 130 m. They have been observed actively feeding in water 35-45 m deep (Uspenski 1956). However, in Kattegatt, Denmark, approximately 80% of all Black Guillemots were recorded in water with depths of 10-30 m (Durinck et al. 1994). Black Guillemots were always recorded less than 5 km from the coast of Caithness, Scotland during May-July (BirdLife International 2000). At the Bay of Fundy, Canada, almost all birds remained within 300 m of the shore (Ronconi and St. Clair 2002). At Papa Westray, Scotland, the mean foraging distance was 2.4 km away from the colony, and birds were recorded foraging in areas up to 3.9 km away from the colony, but despite this large variation in foraging range, feeding sites were never located further than 1.5 km from the shore (BirdLife International 2000). At Rockabill, Ireland, birds forage within 1 km of the colony or else fly 7km or more to reach the mainland coast (BirdLife International 2000). In the eastern Canadian Arctic, censuses indicated that most birds were feeding within 13 km of breeding colonies, with a few found as far as 15 km (BirdLife International 2000). Sightings were frequently highest within 5 km of the colony (BirdLife International 2000). Several studies (at the Bay of Fundy, Finland, Denmark and Iceland) found that Black Guillemots foraged between 0.5 and 4 km from nest sites, and occasionally beyond 7 km away (BirdLife International 2000). By contrast, in the NW Territories, Canada, breeding adults rarely foraged close to the colony, and some birds may have been travelling as far as 55 km (BirdLife International 2000). Birds probably capture some prey in the water column, but forage principally on benthic prey (Cairns 1987a). In Shetland, birds tend to forage where the sea bed is rocky and vegetated with dense stands of kelp (Laminaria spp.) (Ewins 1990) which reflects the habitat preferences of their main prey (BirdLife International 2000).|
|Continuing decline in area, extent and/or quality of habitat:||Unknown|
|Generation Length (years):||10.9|
|Movement patterns:||Full Migrant|
|Congregatory:||Congregatory (and dispersive)|
|Major Threat(s):||The following information refers to the species's European range only: This species is likely to be susceptible to the impacts of climate change, such as sea temperature rise and shifts in prey distribution and abundance. The species is vulnerable to oil spills and other marine pollution (HELCOM 2013, Nettleship et al. 2013). At the breeding colonies the species is vulnerable to invasive predators, such as rats, cats, and American Mink (Neovison vison) (HELCOM 2013). The species is susceptible to being caught in gillnets (Fangel et al. 2011, Žydelis et al. 2013), although other fishing gears may also catch significant numbers. Increasing numbers of offshore wind farms may result in displacement from habitat, and a low risk of collision (Bradbury et al. 2014). It is hunted for consumption in parts of Scandinavia (Mendel et al. 2008).|
Conservation Actions Underway
The following information refers to the species's European range only: The species is listed within the African Eurasian Waterbird Agreement. There are 91 marine Important Bird Areas which include this species in Europe. Within the EU the species is listed within 29 Special Protection Areas. It is listed as Near Threatened by the HELCOM Convention.
Conservation Actions Proposed
The following information refers to the species's European range only: Further identification of important sites for this species, particularly in offshore regions and designation as marine protected areas; Identify the risks of different activities on seabirds, and locations sensitive to seabirds. Continue eradication of invasive predators from breeding colonies. Management of fisheries to ensure long term sustainability of key stocks (e.g. sandeels). Establish observer schemes for bycatch and prepare National/European Community plans of action on seabird bycatch. Develop codes-of-conduct for more organised activities (e.g. tourism). Ensure that appropriate protection (national laws and international agreements) applies to new areas and times in cases of changes in seabird migration routes and times.
|Citation:||BirdLife International. 2016. Cepphus grylle. The IUCN Red List of Threatened Species 2016: e.T22694861A86848264.Downloaded on 25 June 2018.|
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