LC
Common Murre Uria aalge



Justification

Justification of Red List Category
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 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 extremely 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.

Population justification
The global population is estimated to number >18,000,000 individuals (del Hoyo et al. 1996). The European population is estimated at 2,350,000-3,060,000 mature individuals (BirdLife International 2015).

Trend justification
In North America, the population is increasing (based on BBS/CBC data: Butcher and Niven 2007). Although a number of populations in Europe are increasing, including in the UK (which holds nearly half the European population) since 2000 (JNCC 2014), a recent sharp decline was observed in Iceland (where nearly a quarter of the European population is found) since 2005. As a result of the reported decline in Iceland, the estimated and projected rate of decline of the European population size over the period 2005-2050 (three generations) varies from 25% to more than 50% (BirdLife International 2015).

Distribution and population

This species has a circumpolar distribution, occurring in the low-arctic and boreal waters of the North Atlantic and North Pacific (del Hoyo et al. 1996).

Ecology

Behaviour The Common Murre is a pursuit-diving marine bird which forages primarily during daylight. One parent remains at the colony with the chick whilst the other is on a foraging trip. Birds departing colonies usually splash-down to form large rafts close to the colony before departing to foraging areas. External radio tagging has been shown to adversely effect breeding, whereas birds fitted with internal transmitters behaved as normal (Wanless et al. 1988, Nevins 2004).
Diet During the breeding season, schooling pelagic fish species are the most important prey for adults, though benthic species can also be important. In Labrador, Canada, shannies (Sticheaidae) were the main source of food, comprising 84% of the diet in 1996 and 52.9% in 1997 (Bryant and Jones 1999). Capelin (Mallotus villosus) were also important, forming 44.7% of the diet in 1997 (Bryant and Jones 1999). In the UK, the main prey taxa are sandeel (Ammodytes spp.) and clupeids. Small gadoids are also important at some colonies.
Foraging range This species dives to maximum depths of 170-230 m. During the breeding season, surveys recorded the highest densities of birds in the 51 - 100 m depth zone, although birds were still abundant in water less than 50 m and 101 - 200 m deep. Very few were seen in deeper areas (Wanless et al. 1990). The foraging range of this species appears variable across seasons and years. At the Isle of May, Scotland, during 1986 around 70% of foraging trips were over 7 km from the colony, whereas in the following year the birds tended to make shorter trips (Wanless et al. 1990). Foraging trips in eastern Canada are within 100 km (Cairns et al. 1987, Davoren et al. 2003), and in Pribilof Islands, Alaska, foraging occurred mostly within 60 km. In Witless Bay, Newfoundland, foraging aggregations formed over large Capelin schools within 5 km of breeding sites. Along the Newfoundland coastline, aggregations occurred within 15 km of the colonies, and at an offshore ridge about 80 km southeast of the colonies. Despite these large foraging radii, waters close to the colony were the most frequent destination of feeding birds. This was particularly true during chick rearing, when only one third of feeding trips could have exceeded 10 km from the colony (Cairns et al. 1987). In Pribilof Islands, Alaska, birds showed a consistent preference for shallower waters (Schneider and Hunt 1984). High densities of foraging birds have also been observed foraging over a submarine ridge (Coyle et al. 1992). In Kachemak Bay, Alaska, it appears that birds tend to feed over rocky substrates in water depths of about 18 to 55 m (Sanger 1987). They have also been observed to forage in riptides (Wanless et al. 1990), and in areas of sandy sediment suitable for sandeels (Wanless et al. 1998, BirdLife International 2000). Near Flamborough Head, UK, the Farallones, California, and Pribilof Islands, Alaska, birds forage at fronts between thermally distinct bodies of water. In the UK, this occurs at a seasonally-occuring front between thermally-mixed and thermally-stratified water, whereas in the Farallones, the front was between cold and salty upwellings and estuarine outflow (Decker and Hunt 1996, BirdLife International 2000).

Threats

This species is in direct competition with fisheries for food and, as such, overfishing of certain stocks appears to have direct impacts on Common Murres. The collapse of the Barents Sea capelin stock led to an 85% reduction in the breeding population on Bear Island with no signs of recovery (Nettleship et al. 2018). Mortality due to unregulated gill-net fisheries may also be significant (Nettleship et al. 2018). Oil pollution from vessels sunk during World War II is thought to be responsible for the sharp decline in Irish Sea colonies during the mid-20th century, from which the affected populations are yet to recover fully (Birkhead 2016). Hunting in the Faeroes, Greenland and Newfoundland is unregulated and may be occurring at unsustainable levels. No formal assessment has been made of sustainable harvest levels for this species (Nettleship et al. 2018). The Common Murre is also sensitive to variations in sea surface temperature, with a 1˚C change in temperature linked to an annual population decline of c.10% (Irons et al. 2008).

Conservation actions

Conservation Actions Underway
Uria aalge ibericus is found on Annex I of the EU Birds Directive. With the implementation of bird protection laws, a slow recovery occurred over much of the Atlantic breeding range up to the early 1970s except in north Norway, the Faeroes and probably Iceland (Nettleship et al. 2018).

Conservation Actions Proposed
At major colonies, detailed monitoring is needed, particularly in Iceland, which suffered a large decline post-2005 (Nettleship et al. 2018). The impact of bycatch in fish nets can be reduced in several ways: Protecting areas on a seasonal and/or diurnal scale; concentrating salmon fisheries when salmon densities are high to improve fishing efficiency and catch to bycatch ratios; changing to an alternative fishing technique may reduce seabird mortality; and gear modification (Österblom et al. 2002).

Acknowledgements

Text account compilers
Calvert, R., Ekstrom, J., Hatchett, J., Ashpole, J, Butchart, S., Stuart, A., Fjagesund, T., Martin, R.


Recommended citation
BirdLife International (2019) Species factsheet: Uria aalge. Downloaded from http://www.birdlife.org on 18/09/2019. Recommended citation for factsheets for more than one species: BirdLife International (2019) IUCN Red List for birds. Downloaded from http://www.birdlife.org on 18/09/2019.