Uria lomvia -- (Linnaeus, 1758) - BirdLife...

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Uria lomvia -- (Linnaeus, 1758) ANIMALIA -- CHORDATA -- AVES -- CHARADRIIFORMES -- ALCIDAE Common names: Thick-billed Murre; Brünnich's Guillemot European Red List Assessment European Red List Status LC -- Least Concern, (IUCN version 3.1) Assessment Information Year published: 2015 Date assessed: 2015-03-31 Assessor(s): BirdLife International Reviewer(s): Symes, A. Compiler(s): Ashpole, J., Burfield, I., Ieronymidou, C., Pople, R., Wheatley, H. & Wright, L. Assessment Rationale European regional assessment: Least Concern (LC) EU27 regional assessment: Not Evaluated (NE) The range size has not been quantified, but it is not believed to approach the thresholds for Vulnerable under the population size criterion (10% in ten years or three generations, or with a specified population structure). The population size is extremely large, and hence does not approach the thresholds for Vulnerable under the population size criterion (10% in ten years or three generations, or with a specified population structure). The population trend is not known, but the population is not believed to be decreasing sufficiently rapidly to approach the thresholds under the population trend criterion (30% decline over ten years or three generations). For these reasons the species is evaluated as Least Concern in Europe. The species is Not Evaluated (NE) for the EU27 region as winter (non-breeding season) data were not available. Occurrence Countries/Territories of Occurrence Native: Faroe Islands (to DK); Greenland (to DK); Iceland; Norway; Svalbard and Jan Mayen (to NO); Russian Federation Vagrant: Austria; Belgium; Denmark; Finland; France; Germany; Ireland, Rep. of; Latvia; Netherlands; Poland; Portugal; Romania; Spain; Sweden; United Kingdom Population The European population is estimated at 1,920,000-2,840,000 mature individuals. The species does not occur in the EU27. For details of national estimates, see Supplementary PDF . Trend In Europe the population size trend is unknown. For details of national estimates, see Supplementary PDF . Habitats and Ecology The species is exclusively marine, occurring offshore and along sea coasts. It breeds on coastal cliffs and islands, and is almost completely restricted to high and low Arctic zones with open water and adequate summer food supply (Nettleship and Christie 2013). It avoids extensive permanent pack-ice, breeding only in areas where vigorous vertical circulation creates open water supporting rich planktonic biomass near cliffed coasts (Snow and Perrins 1998). It winters mostly offshore to the edge of the continental shelf, and along sea coasts and in bays where concentrations of fish and invertebrates occur. At sea it is found in flocks which are often large, likely related to the non-random distribution of winter prey. Colony locations are usually associated with dynamic water systems, for example fronts, upwellings and converging currents where primary and secondary productivity is high. Arrival at breeding colonies and start of laying are variable and usually related to sea temperatures; towards the southern limit of low Arctic water and in northern boreal

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Page 1: Uria lomvia -- (Linnaeus, 1758) - BirdLife Internationaldatazone.birdlife.org/.../erlob/summarypdfs/22694847_uria_lomvia.pdf · Uria lomvia -- (Linnaeus, 1758) ANIMALIA -- CHORDATA

Uria lomvia -- (Linnaeus, 1758)ANIMALIA -- CHORDATA -- AVES -- CHARADRIIFORMES -- ALCIDAECommon names: Thick-billed Murre; Brünnich's Guillemot

European Red List AssessmentEuropean Red List Status

LC -- Least Concern, (IUCN version 3.1)

Assessment InformationYear published: 2015Date assessed: 2015-03-31Assessor(s): BirdLife InternationalReviewer(s): Symes, A.Compiler(s): Ashpole, J., Burfield, I., Ieronymidou, C., Pople, R., Wheatley, H. & Wright, L.Assessment RationaleEuropean regional assessment: Least Concern (LC)EU27 regional assessment: Not Evaluated (NE)

The range size has not been quantified, but it is not believed to approach the thresholds for Vulnerable under the population size criterion (10% in ten years or three generations, or with a specified population structure). The population size is extremely large, and hence does not approach the thresholds for Vulnerable under the population size criterion (10% in ten years or three generations, or with a specified population structure). The population trend is not known, but the population is not believed to be decreasing sufficiently rapidly to approach the thresholds under the population trend criterion (30% decline over ten years or three generations). For these reasons the species is evaluated as Least Concern in Europe.

The species is Not Evaluated (NE) for the EU27 region as winter (non-breeding season) data were not available.

OccurrenceCountries/Territories of OccurrenceNative:Faroe Islands (to DK); Greenland (to DK); Iceland; Norway; Svalbard and Jan Mayen (to NO); Russian FederationVagrant:Austria; Belgium; Denmark; Finland; France; Germany; Ireland, Rep. of; Latvia; Netherlands; Poland; Portugal; Romania; Spain; Sweden; United Kingdom

PopulationThe European population is estimated at 1,920,000-2,840,000 mature individuals. The species does not occur in the EU27. For details of national estimates, see Supplementary PDF.

TrendIn Europe the population size trend is unknown. For details of national estimates, see Supplementary PDF.

Habitats and EcologyThe species is exclusively marine, occurring offshore and along sea coasts. It breeds on coastal cliffs and islands, and is almost completely restricted to high and low Arctic zones with open water and adequate summer food supply (Nettleship and Christie 2013). It avoids extensive permanent pack-ice, breeding only in areas where vigorous vertical circulation creates open water supporting rich planktonic biomass near cliffed coasts (Snow and Perrins 1998). It winters mostly offshore to the edge of the continental shelf, and along sea coasts and in bays where concentrations of fish and invertebrates occur. At sea it is found in flocks which are often large, likely related to the non-random distribution of winter prey. Colony locations are usually associated with dynamic water systems, for example fronts, upwellings and converging currents where primary and secondary productivity is high. Arrival at breeding colonies and start of laying are variable and usually related to sea temperatures; towards the southern limit of low Arctic water and in northern boreal

Page 2: Uria lomvia -- (Linnaeus, 1758) - BirdLife Internationaldatazone.birdlife.org/.../erlob/summarypdfs/22694847_uria_lomvia.pdf · Uria lomvia -- (Linnaeus, 1758) ANIMALIA -- CHORDATA

waters laying takes place late May to early June, in more northerly locations laying later in June or July. The species is highly colonial, usually in immense aggregations and at high densities on steep sea cliffs. The single egg is laid directly onto bare rock on narrow cliff ledges. It feeds on fish, squid and crustaceans throughout the year, supplemented by polychaetes and molluscs (Nettleship and Christie 2013). In low-Arctic Greenland and in the European sector of the polar basin, part of the population is present year round though some birds, notably immatures, move away in autumn (Snow and Perrins 1998). Birds from west Greenland move south to east Newfoundland (shelf and Grand Banks) and Nova Scotia. Birds from the European Arctic move south-west towards west Greenland, including Spitsbergen birds that reach both south-west Greenland and Newfoundland waters (Nettleship and Christie 2013).Habitats & Altitude

Habitat (level 1 - level 2) Importance OccurrenceMarine Coastal/Supratidal - Sea Cliffs and Rocky Offshore Islands major breedingMarine Neritic - Macroalgal/Kelp major breedingMarine Neritic - Macroalgal/Kelp major non-breedingMarine Neritic - Pelagic major breedingMarine Neritic - Pelagic major non-breedingMarine Neritic - Seagrass (Submerged) major breedingMarine Neritic - Seagrass (Submerged) major non-breedingMarine Neritic - Subtidal Loose Rock/pebble/gravel major breedingMarine Neritic - Subtidal Loose Rock/pebble/gravel major non-breedingMarine Neritic - Subtidal Rock and Rocky Reefs major breedingMarine Neritic - Subtidal Rock and Rocky Reefs major non-breedingMarine Neritic - Subtidal Sandy major breedingMarine Neritic - Subtidal Sandy major non-breedingMarine Neritic - Subtidal Sandy-Mud major breedingMarine Neritic - Subtidal Sandy-Mud major non-breedingMarine Oceanic - Epipelagic (m) suitable breedingMarine Oceanic - Epipelagic (m) suitable non-breedingAltitude Occasional altitudinal limits

ThreatsThe species suffers from incidental kills in fishing nets, competition with commercial fisheries, notably in Barents Sea, Iceland and oil pollution and offshore oil developments in many areas (e.g,. Barents Sea, North Sea) (Nettleship and Christie 2013). It is also likely to be affected by climate change (Gaston et al. 2005).Threats & Impacts

Threat (level 1) Threat (level 2) Impact and StressesBiological resource use

Fishing & harvesting aquatic resources (unintentional effects: (large scale) [harvest])

Timing Scope Severity ImpactOngoing Unknown Unknown Unknown

StressesSpecies mortality; Competition

Climate change & severe weather

Habitat shifting & alteration

Timing Scope Severity ImpactFuture Whole (>90%) Unknown Unknown

StressesEcosystem degradation; Indirect ecosystem effects

Climate change & severe weather

Temperature extremes

Timing Scope Severity ImpactOngoing Unknown Unknown Unknown

StressesSpecies mortality; Reduced reproductive success

Energy production & mining

Oil & gas drilling Timing Scope Severity ImpactOngoing Majority (50-90%) Unknown Unknown

StressesEcosystem conversion; Ecosystem degradation

Invasive and other problematic species, genes & diseases

Red Fox (Vulpes vulpes)

Timing Scope Severity ImpactOngoing Minority (<50%) Unknown Unknown

StressesSpecies mortality

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Threats & ImpactsThreat (level 1) Threat (level 2) Impact and Stresses

Pollution Oil spills Timing Scope Severity ImpactOngoing Majority (50-90%) Unknown Unknown

StressesEcosystem degradation; Indirect ecosystem effects; Species mortality

ConservationConservation Actions UnderwayThere are no known current conservation measures for this species.

Conservation Actions ProposedThere are a number of immediate conservation requirements for this species. Enhanced monitoring of major colonies is needed, particularly in Iceland, Spitsbergen and the Russian Arctic, where population size and status are inadequately known. Detailed assessment of impacts of overfishing by commercial fisheries is required, particularly of capelin, cod, herring and sand eels in the Barents Sea and Iceland. Continue and expand assessments of by-catch in gill-net fisheries, particularly in the NE Atlantic. Tighter legislation and penalties (national and international) associated with oil pollution from offshore developments and transport, as well as expansion and refinement of monitoring schemes to assess bird mortality should be developed. The eradication of alien predators, especially foxes at Russian colonies should be undertaken (Nettleship and Christie 2013).

BibliographyGaston, A.J., Gilchrist, H. G., and Hipfner, J. 2005. Climate change, ice conditions and reproduction in an Arctic nesting marine bird: Brunnich's guillemot (Uria lomvia L.). Journal of Animal Ecology, 74(5), 832-841.Nettleship, D.N. and Christie, D.A. 2013. Thick-billed Murre (Uria lomvia). In: del Hoyo, J., Elliott, A., Sargatal, J., Christie, D.A. and de Juana, E. (eds.) 2013. Handbook of the Birds of the World Alive. Lynx Edicions, Barcelona. (retrieved from http://www.hbw.com/node/54061 on 15 October 2014).Snow, D.W. and Perrins, C.M. 1998. The Birds of the Western Palearctic vol. 1: Non-Passerines. Oxford University Press, Oxford.

Map (see overleaf)

Page 4: Uria lomvia -- (Linnaeus, 1758) - BirdLife Internationaldatazone.birdlife.org/.../erlob/summarypdfs/22694847_uria_lomvia.pdf · Uria lomvia -- (Linnaeus, 1758) ANIMALIA -- CHORDATA