Podiceps cristatus 


Taxonomy [top]

Kingdom Phylum Class Order Family
Animalia Chordata Aves Podicipediformes Podicipedidae

Scientific Name: Podiceps cristatus
Species Authority: (Linnaeus, 1758)
Regional Assessments:
Common Name(s):
English Great Crested Grebe
French Grèbe huppé
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.

Assessment Information [top]

Red List Category & Criteria: Least Concern ver 3.1
Year Published: 2012
Date Assessed: 2012-05-01
Assessor(s): BirdLife International
Reviewer(s): Butchart, S. & Symes, A.
Facilitator/Compiler(s): Ekstrom, J., Butchart, S., Malpas, L., Calvert, R.
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 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). 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:
2009 Least Concern (LC)
2008 Least Concern (LC)
2004 Least Concern (LC)
2000 Lower Risk/least concern (LR/lc)
1994 Lower Risk/least concern (LR/lc)
1988 Lower Risk/least concern (LR/lc)

Geographic Range [top]

Range Description: The Great Crested Grebe is found across most of Europe and central Asia, though it also winters in parts of southern Asia (e.g. northern India). Colonies can also be found scattered through Africa, from Tunisia and Egypt in the north, through a few scattered colonies in central Africa to South Africa. Nesting colonies are also found in southern Australia and New Zealand, with individuals wintering in eastern and northern Australia (del Hoyo et al. 1992).
Countries occurrence:
Afghanistan; Albania; Algeria; Angola (Angola); Armenia (Armenia); Australia; Austria; Azerbaijan; Bahrain; Bangladesh; Belarus; Belgium; Bhutan; Bosnia and Herzegovina; Botswana; Bulgaria; China; Congo, The Democratic Republic of the; Croatia; Cyprus; Czech Republic; Denmark; Egypt; Estonia; Ethiopia; Finland; France; Gabon; Georgia; Germany; Greece; Hong Kong; Hungary; India; Iran, Islamic Republic of; Iraq; Ireland; Israel; Italy; Japan; Jordan; Kazakhstan; Kenya; Korea, Democratic People's Republic of; Korea, Republic of; Kuwait; Kyrgyzstan; Latvia; Lebanon; Libya; Liechtenstein; Lithuania; Luxembourg; Macedonia, the former Yugoslav Republic of; Malta; Moldova; Monaco; Mongolia; Montenegro; Morocco; Mozambique; Myanmar; Namibia; Nepal; Netherlands; New Zealand; Norway; Pakistan; Poland; Portugal; Qatar; Romania; Russian Federation; Rwanda; San Marino; Saudi Arabia; Serbia (Serbia); Slovakia; Slovenia; South Africa; Spain; Sweden; Switzerland; Syrian Arab Republic; Taiwan, Province of China; Tajikistan; Tanzania, United Republic of; Thailand; Tunisia; Turkey; Turkmenistan; Uganda; Ukraine; United Kingdom; Uzbekistan; Zambia; Zimbabwe
Burundi; Faroe Islands; Gambia; Iceland; Indonesia; Lesotho; Mali; Nigeria; Oman; Senegal; Swaziland; United Arab Emirates
Present - origin uncertain:
Continuing decline in area of occupancy (AOO): Unknown
Extreme fluctuations in area of occupancy (AOO): No
Estimated extent of occurrence (EOO) - km2: 28300000
Continuing decline in extent of occurrence (EOO): Unknown
Extreme fluctuations in extent of occurrence (EOO): No
Continuing decline in number of locations: Unknown
Extreme fluctuations in the number of locations: No
Upper elevation limit (metres): 3000
Range Map: Click here to open the map viewer and explore range.

Population [top]

Population: The global population is estimated to number c.920,000-1,400,000 individuals (Wetlands International 2006), while national population estimates include: c.100-10,000 breeding pairs, c.50-1,000 individuals on migration and c.1,000-10,000 wintering individuals in China; < c.50 individuals on migration and c.50-1,000 wintering individuals in Taiwan; c.100-10,000 breeding pairs, c.50-1,000 individuals on migration and c.1,000-10,000 wintering individuals in Korea; c.100-10,000 breeding pairs, c.50-1,000 individuals on migration and c.1,000-10,000 wintering individuals in Japan and c.10,000-100,000 breeding pairs and c.1,000-10,000 individuals on migration in Russia (Brazil 2009).

Trend Justification:  The overall population trend is uncertain, as some populations are decreasing, while others are increasing or have unknown trends (Wetlands International 2006).
Current Population Trend: Unknown
Additional data:
Continuing decline of mature individuals: Unknown
Extreme fluctuations: No Population severely fragmented: No
Continuing decline in subpopulations: Unknown
Extreme fluctuations in subpopulations: No All individuals in one subpopulation: No

Habitat and Ecology [top]

Habitat and Ecology: Behaviour The majority of this species is fully migratory although some populations may only undergo local dispersive movements (del Hoyo et al. 1992). It breeds between April and September in Europe, in all months of the year in Africa (peaking during long rainy season) and from November to March in Australasia, nesting either in solitary, dispersed pairs or in loose colonies (del Hoyo et al. 1992) (forming only where safe nesting sites are few and feeding areas are extensive) (Fjeldsa 2004). After breeding (from August to October) (Fjeldsa 2004) adults may disperse locally to large lakes and reservoirs to undergo a flightless moulting period (del Hoyo et al. 1992), during which gatherings of hundreds of individuals(occasionally even greater than 10,000) may form (Fjeldsa 2004). During the winter the species largely remains solitary (Snow and Perrins 1998), especially when feeding (Fjeldsa 2004), but temporary congregations (Snow and Perrins 1998) of up to 5,000 individuals may form in some areas (Fjeldsa 2004).Habitat Breeding The species breeds on fresh or brackish waters with abundant emergent and submerged vegetation (del Hoyo et al. 1992, Snow and Perrins 1998), showing a preference for non-acidic eutrophic waterbodies with flat or sloping banks and muddy or sandy substrates (Snow and Perrins 1998), usually 0.5-5 m deep (Snow and Perrins 1998) and with large areas of open water (del Hoyo et al. 1992). Suitable habitats include small pools or lakes, backwaters of slow-flowing rivers and artificial waterbodies (e.g. reservoirs, fish-ponds, gravel pits and ornamental lakes) (del Hoyo et al. 1992). In Australia the species also utilises swamps, reservoirs, lagoons, salt-fields, estuaries and bays (Marchant and Higgins 1990), and in tropical Africa and New Zealand it may breed on montane, subalpine and alpine lakes up to 3,000 m (del Hoyo et al. 1992). Non-breeding The species overwinters on large exposed ice-free (Fjeldsa 2004) lakes and reservoirs (del Hoyo et al. 1992, Snow and Perrins 1998), moving to sheltered coastal inshore waters (Snow and Perrins 1998) less than 10 m deep (Fjeldsa 2004) such as brackish estuaries (del Hoyo et al. 1992, Snow and Perrins 1998), deltas, tidal channels and tidal lagoons (Snow and Perrins 1998) during cold spells (Fjeldsa 2004). In addition it frequents large saline lakes in Australia (Marchant and Higgins 1990). Diet Its diet consists predominantly of large fish as well as insects, crustaceans (e.g. crayfish, shrimps) and molluscs, occasionally also adult and larval amphibians (del Hoyo et al. 1992). The species's invertebrate consumption is highest during the breeding season (del Hoyo et al. 1992). Breeding site The nest is a platform of aquatic plant matter either floating on water and anchored to emergent vegetation or built from the lake bottom in shallow water (del Hoyo et al. 1992). Typical nest sites include reedbeds or flooded thickets as well as more open sites such as floating mats of water-weed or kelp fronds (Fjeldsa 2004).
Systems: Terrestrial; Freshwater; Marine
Continuing decline in area, extent and/or quality of habitat: Unknown
Generation Length (years): 7.1
Movement patterns: Full Migrant
Congregatory: Congregatory (and dispersive)

Threats [top]

Major Threat(s): The species suffered declines in the nineteenth century as a result of hunting for the plume trade (this is no longer a threat) (del Hoyo et al. 1992). The species was also hunted in the past for food in New Zealand, a threat that although past is still limiting to the New Zealand population when combined with the modern threats of low food availability, modification of lakes for recreational purposes (del Hoyo et al. 1992), hydroelectric development and the introduction of competitors (e.g. trout) and predators (e.g. weasels, cats and rats) (Fjeldsa 2004). The species is commonly drowned accidentally in monofilament gill-nets (fishing nets) (del Hoyo et al. 1992, Fjeldsa 2004) with mesh sizes greater than 5 cm (Quan et al. 2002). It may also be threatened by future coastal oil spills (Gorski et al. 1977), and is susceptible to avian influenza so may be threatened by future outbreaks of the virus (Melville and Shortridge 2006). Utilisation The species is hunted for commercial (food) and recreational purposes in Iran (Balmaki and Barati 2006).

Citation: BirdLife International. 2012. Podiceps cristatus. The IUCN Red List of Threatened Species 2012: e.T22696602A40218602. . Downloaded on 29 May 2016.
Disclaimer: To make use of this information, please check the <Terms of Use>.
Feedback: If you see any errors or have any questions or suggestions on what is shown on this page, please provide us with feedback so that we can correct or extend the information provided