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Taxon ID: 40,664 Total records: 39,143

Otis tarda

Classification

Kingdom Animalia (COL)
Phylum Chordata (COL)
Class Aves (COL)
Order Gruiformes (COL)
Family Otididae (COL)

Taxonomy

Genus Otis Reference
SubGenus Vernacular Name
Species tarda IUCN Threat Status-Year Vulnerable, 2015
SubSpecies Nat'l Threat Status-Year Not Evaluated, 2000
Infraspecies Reason for Change
Infraspecies Rank CITES
Taxonomic Group Birds Native Status Not known
Scientific Name Author Linnaeus,1758 Country Distribution Myanmar
Citation Description Geographic Range [top] Range Description: Otis tarda breeds in Morocco (91-108 birds), Portugal (1,893 birds), Spain (29,400 - 34,300 birds), Austria (199-216 birds), Czech Republic (0-2 birds), Germany (114-116 birds), Slovakia (0-3 birds), Hungary (1,413-1,582 birds), Serbia and Montenegro (35-36 birds), Romania (0-8 birds), Turkey (400-1,000 birds), Iran (89-161 birds), Russia (8,000-12,000 birds), Ukraine (520 -680 birds), Kazakhstan (0-300 birds), Mongolia (c.1,000 birds [Palacín and Alonso 2008]), and China (c.500-3,300 birds [Chan and Goroshko 1998, Alonso and Palacín 2010, M. Kessler in litt. 2012]); and a reintroduction scheme is currently taking place in the United Kingdom. Its Palearctic range is becoming increasingly disjunct and there have been rapid declines and some extinctions throughout eastern and central Europe (Bulgaria, Poland, Moldova [Palacín and Alonso 2008]). Numbers have almost certainly declined in Czech Republic, Slovakia, Romania, Bulgaria, Poland, Moldova, Kazakhstan, Mongolia, Turkey, Iran, and Morocco, and in most of the eastern distribution range (Chan and Goroshko 1998, Barati and Amerifar 2008, Palacín and Alonso 2008), along a with a range contraction due to the disappearance of smaller populations across the speciess range (e.g. in Iberia [Alonso et al. 2003, Alonso et al. 2004] and Hungary [Faragó 1993]). In contrast, the species has increased in Hungary, Austria, and Germany, and there are possible increases in Spain and Portugal (Alonso and Palacín 2010). The previous fluctuating trend in Russia has changed to a rapid decrease during recent years (Antonchikov 2008, 2011). Recent trends are unknown in Ukraine and some parts of Asia. The world population is estimated to be between 44,054 and 57,005 individuals, of which c1,900-4,600 occur in east Asia (Alonso and Palacín 2010). Most populations are partially migratory and 8,000-10,000 birds occur on passage or in winter in Ukraine (Y. Andryucshenko in litt. 1999). Countries occurrence: Native: Afghanistan; Armenia (Armenia); Austria; Azerbaijan; Bulgaria; China; Croatia; Czech Republic; Georgia; Germany; Greece; Hungary; Iran, Islamic Republic of; Iraq; Italy; Kazakhstan; Kyrgyzstan; Macedonia, the former Yugoslav Republic of; Moldova; Mongolia; Montenegro; Morocco; Portugal; Romania; Russian Federation; Serbia (Serbia); Slovakia; Spain; Syrian Arab Republic; Tajikistan; Turkey; Turkmenistan; Ukraine; Uzbekistan Regionally extinct: Belarus; Poland Reintroduced: France Vagrant: Albania; Belgium; Cyprus; Denmark; Egypt; Finland; Gibraltar; Ireland; Israel; Japan; Korea, Democratic Peoples Republic of; Korea, Republic of; Latvia; Lebanon; Luxembourg; Malta; Netherlands; Pakistan; Saudi Arabia; Tunisia Additional data: ? Continuing decline in area of occupancy (AOO): Yes ? Extreme fluctuations in area of occupancy (AOO): No ? Estimated extent of occurrence (EOO) - km2: 440000 ? Continuing decline in extent of occurrence (EOO): Yes ? Extreme fluctuations in extent of occurrence (EOO): No ? Number of Locations: 11-100 ? Continuing decline in number of locations: Yes ? Extreme fluctuations in the number of locations: No Range Map: Click here to open the map viewer and explore range. Population [top] Population: Alonso and Palacín (2010) estimate the global population to number 44,054-57,005 individuals, rounded here to 44,000-57,000 individuals. Trend Justification: Despite a lack of accurate data on trends in several countries with important populations (e.g. Russia, Mongolia, China, Turkey, Ukraine), a rapid and on-going population decline is suspected overall, owing to habitat loss and fragmentation for agricultural intensification, as well as hunting and collision with power lines. Should research show the species to be declining at a more moderate rate, it would warrant downlisting to a lower threat category. Current Population Trend: Decreasing Additional data: ? Continuing decline of mature individuals: Yes ? Extreme fluctuations: No ? Population severely fragmented: No ? No. of subpopulations: 2-100 ? Continuing decline in subpopulations: Yes ? Extreme fluctuations in subpopulations: No ? All individuals in one subpopulation: No Habitat and Ecology [top] Habitat and Ecology: It occurs in open, flat or somewhat rolling landscapes, usually with a mixture of crops (cereals, vineyards, fodder plants, in some countries also with steppic grassland [J. C. Alonso in litt. 2012]). Areas with little or no disturbance and abundant supply of insects are required for successful breeding (Y. Andryucshenko in litt. 1999). Nest sites are selected in fallow or cereal fields (primarily alfalfa in Central Europe) in areas of low patch-type diversity, far from human infrastructure and with good horizontal visibility (Magaña et al. 2010). Highly variable migratory behaviour across populations, including obligate winter migrants (Asia, Russia), facultative migrants (central European populations) and partial winter and summer migrants with differential migratory pattern by sex (Iberian populations) (Morales et al. 2000, Alonso et al. 2000, 2001, Palacín et al. 2009, 2011) Systems: Terrestrial Continuing decline in area, extent and/or quality of habitat: Yes Generation Length (years): 10 Movement patterns: Full Migrant Threats [top] Major Threat(s): Key threats are increased habitat degradation, fragmentation and loss due to agricultural intensification, land-use changes and infrastructure development which has the potential to increase following land privatisation in eastern Europe (S. Nagy in litt. 1999, 2007, Nagy 2009) and is occurring in China (Chan and Goroshko 1998). Habitat loss and fragmentation continues as a result of ploughing of grasslands, intensive grazing, afforestation and increasing development of irrigation schemes, roads, power-lines, fencing and ditches. Mechanisation, chemical fertilisers and pesticides, fire and predation all contribute to high mortality in eggs, chicks, juveniles and incubating females (Nagy 2009). Hunting is a major threat in Morocco, Syria, Turkey, Ukraine, China, Kazakhstan and Mongolia (Y. Andryucshenko in litt. 1999, Chan and Goroshko 1998, P. Goriup in litt. 2007, M. Kessler in litt. 2012) and is expected to intensify as the paved road network in Mongolia expands. Collision with power lines (J. C. Alonso in litt. 2007, Nagy 2009, M. Kessler in litt. 2012) and wind turbines are also significant threats (S. Nagy in litt. 2012). Conservation Actions [top] Conservation Actions: Conservation Actions Underway CITES Appendix I and II, CMS Appendix I and II and CMS MoU in place since 2002. EU Wild Birds Directive Annex I, Bern Convention Annex II, Bonn Convention Annex I (S. Nagy in litt. 1999, 2007, P. Goriup in litt. 2007). A European action plan was published in 1996 and updated in 2009 (Nagy 2009) and an action plan for east Asian populations in 1998. Agri-environmental and land management programmes have been (successfully) implemented in Spain, Portugal, Austria, Hungary, Germany, Serbia. Artificial incubation and chick rearing projects have been established in Germany and Hungary since the 1970s. A UK reintroduction project began in 2003 with chicks imported from the Russian Federation (Dawes 2008). A LIFE Nature project for the species was implemented in Hungary during 2004-2008 with the aim of increasing in-situ protection of the species (Bankovics and Lóránt 2008). Other LIFE projects for the species have been implemented in Spain, Portugal, Germany, Austria and Slovakia. Conservation Actions Proposed Conduct nationwide surveys in countries with currently low quality estimates, to confirm worldwide numbers and trends. Research limiting factors. Research wintering distribution in Russia, Ukraine and Asia. Protect and manage breeding and wintering areas. Upgrade existing and establish new protected areas in east Asia. Implement agri-environment measures for low-intensity farming. Prevent steppe fires, illegal hunting and collision with power-lines. Raise public awareness. Citation: BirdLife International. 2015. Otis tarda. The IUCN Red List of Threatened Species 2015: e.T22691900A85068116. Downloaded on 28 September 2016. Disclaimer: To make use of this information, please check the . 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Synonyms


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Common Names


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Localities


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Species Record Updated By: Carlos Aurelio Callangan