|Scientific Name:||Otis tarda|
|Species Authority:||Linnaeus, 1758|
|Red List Category & Criteria:||Vulnerable A2cd+3cd+4cd ver 3.1|
|Contributor(s):||Alonso, J. C., Andryucshenko, Y., Antonchikov, A., Goriup, P., Nagy, S. & Kessler, M.|
|Facilitator/Compiler(s):||Benstead, P., Capper, D., Derhé, M., Harding, M., Peet, N. & Symes, A.|
This species has suffered rapid population reductions across most of its range owing to the loss, degradation and fragmentation of its habitat, as well as hunting. Although populations in its Iberian stronghold have stabilised and possibly increased, hunting in Central Asia results in high rates of adult mortality, and land-use changes in eastern Europe, Russia and central Asia may have a significant impact on this species's population and the extent of its remaining habitat, such that it is likely to continue declining at a rapid rate over the next three generations. It therefore qualifies as Vulnerable. Should research show the species to be declining at a more moderate rate, it would warrant downlisting to a lower category of threat.
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 species's 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).
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
Vagrant:Albania; Belgium; Cyprus; Denmark; Egypt; Finland; Gibraltar; Ireland; Israel; Japan; Korea, Democratic People's Republic of; Korea, Republic of; Latvia; Lebanon; Luxembourg; Malta; Netherlands; Pakistan; Saudi Arabia; Tunisia
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||Alonso and Palacín (2010) estimate the global population to number 44,054-57,005 individuals, rounded here to 44,000-57,000 individuals.|
|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)
|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 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 2013. Otis tarda. The IUCN Red List of Threatened Species. Version 2014.3. <www.iucnredlist.org>. Downloaded on 20 December 2014.|
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