The IUCN Red List of Threatened Species™ ISSN 2307-8235 (online) IUCN 2008: T22696038A80351871 Aquila nipalensis, Steppe Eagle Assessment by: BirdLife International View on www.iucnredlist.org Citation: BirdLife International. 2015. Aquila nipalensis. The IUCN Red List of Threatened Species 2015: e.T22696038A80351871. http://dx.doi.org/10.2305/IUCN.UK.20154.RLTS.T22696038A80351871.en Copyright: © 2015 International Union for Conservation of Nature and Natural Resources Reproduction of this publication for educational or other non-commercial purposes is authorized without prior written permission from the copyright holder provided the source is fully acknowledged. Reproduction of this publication for resale, reposting or other commercial purposes is prohibited without prior written permission from the copyright holder. For further details see Terms of Use. The IUCN Red List of Threatened Species™ is produced and managed by the IUCN Global Species Programme, the IUCN Species Survival Commission (SSC) and The IUCN Red List Partnership. The IUCN Red List Partners are: BirdLife International; Botanic Gardens Conservation International; Conservation International; Microsoft; NatureServe; Royal Botanic Gardens, Kew; Sapienza University of Rome; Texas A&M University; Wildscreen; and Zoological Society of London. If you see any errors or have any questions or suggestions on what is shown in this document, please provide us with feedback so that we can correct or extend the information provided. THE IUCN RED LIST OF THREATENED SPECIES™ Taxonomy Kingdom Phylum Class Order Family Animalia Chordata Aves Accipitriformes Accipitridae Taxon Name: Aquila nipalensis Hodgson, 1833 Regional Assessments: • Europe Common Name(s): • English: • French: Steppe Eagle Aigle des steppes 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. Identification Information: 72-81 cm, wingspan 160-200 cm. Dark-brown, medium-large Aquila. Juvenile usually has broad whitish band along greater underwing coverts. Primaries banded, iris brown (Meyburg and Boesman 2013). Similar spp. Larger than Tawny Eagle A. rapax and separated by width and length of gape. Generally darker than Lesser Spotted Eagle A. pomarina and paler than Greater Spotted Eagle A. clanga and has oval nostrils rather than round as in both these species. Assessment Information Red List Category & Criteria: Endangered A2abcd+3bcd+4abcd ver 3.1 Year Published: 2015 Date Assessed: October 1, 2015 Justification: This species has undergone extremely rapid population declines within its European range. The majority of its range lies outside Europe where it was not thought to be declining at a sufficiently rapid rate to approach the threshold for Vulnerable. However recent information suggests that the population outside Europe may be exposed to greater threats than was previously thought and has also undergone very rapid recent declines across much of the range. It is therefore classified as Endangered. Previously Published Red List Assessments 2013 – Least Concern (LC) – http://dx.doi.org/10.2305/IUCN.UK.2013-2.RLTS.T22696038A40710277.en 2012 – Least Concern (LC) 2011 – Least Concern (LC) 2009 – Least Concern (LC) © The IUCN Red List of Threatened Species: Aquila nipalensis – published in 2015. http://dx.doi.org/10.2305/IUCN.UK.2015-4.RLTS.T22696038A80351871.en 1 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 Range Description: This species breeds east of 42°E in European Russia from the Astrakhan to Stavropol regions (Hagermeijer and Blair 1997), across Kazakhstan into Kyrgyzstan, China and Mongolia (Meyburg and Boesman 2013). It also breeds in a small area of Turkey. It formerly bred in Moldova, Romania and Ukraine. Birds from European Russia, eastern Kazakhstan and Turkey (A. n. orientalis) winter in the Middle East, Arabia and east and southern Africa (Meyburg and Boesman 2013). Birds from Altai, Siberia eastwards (A. n. nipalensis) winter mainly in south and south-east Asia. Country Occurrence: Native: Afghanistan; Albania; Armenia (Armenia); Azerbaijan; Bahrain; Bangladesh; Bhutan; Botswana; Bulgaria; China; Congo, The Democratic Republic of the; Djibouti; Egypt; Eritrea; Ethiopia; Georgia; Greece; India; Iran, Islamic Republic of; Iraq; Israel; Jordan; Kazakhstan; Kenya; Kuwait; Kyrgyzstan; Lebanon; Malawi; Malaysia; Mongolia; Myanmar; Namibia; Nepal; Oman; Pakistan; Palestinian Territory, Occupied; Qatar; Russian Federation; Rwanda; Saudi Arabia; Singapore; South Africa; South Sudan; Sudan; Swaziland; Syrian Arab Republic; Tajikistan; Tanzania, United Republic of; Thailand; Turkey; Turkmenistan; Uganda; Ukraine; United Arab Emirates; Uzbekistan; Viet Nam; Yemen; Zambia; Zimbabwe Regionally extinct: Moldova; Romania Vagrant: Angola (Angola); Belarus; Burundi; Cameroon; Chad; Croatia; Czech Republic; Denmark; Estonia; Finland; France; Germany; Hungary; Italy; Korea, Democratic People's Republic of; Mali; Netherlands; Niger; Nigeria; Norway; Poland; Slovakia; Somalia; Spain; Sweden; Tunisia © The IUCN Red List of Threatened Species: Aquila nipalensis – published in 2015. http://dx.doi.org/10.2305/IUCN.UK.2015-4.RLTS.T22696038A80351871.en 2 Distribution Map © The IUCN Red List of Threatened Species: Aquila nipalensis – published in 2015. http://dx.doi.org/10.2305/IUCN.UK.2015-4.RLTS.T22696038A80351871.en 3 Population Even assuming densities as low as one pair / 100 km2 across eight million km2 range there would be 80,000 pairs or 160,000 mature individuals (Ferguson-Lees and Christie 2001). The European population is estimated at 800-1,200 pairs, which equates to 1,600-2,400 mature individuals (BirdLife International 2015). Europe forms approximately 9% of the global range, so a very preliminary estimate of the global population size is 17,800-26,700 mature individuals. The estimate based on the European population is much lower than the 160,000 mature individuals estimated by Ferguson-Lees and Christie (2001) and may be explained by differing densities of the species across its range. Combined totals from across the whole range estimate the number of pairs at 31,372 (26,014-36,731) which equates to 62,744 (52,02873,462) mature individuals or 94,116 (78,042-110,193) individuals (I. Karyakin in litt. 2015). The population is placed in the band 100,000 to 499,999 mature individuals. Trend Justification The population is declining owing to habitat destruction (especially conversion of steppe into agricultural land), persecution, and collisions with power lines. Locally populations are declining owing to heavy predation of chicks (Ferguson-Lees and Christie 2001). In Europe the population size is estimated to be decreasing by 80% or more in 49.8 years (three generations) (BirdLife International 2015) however the European population represents only a small proportion of the global population. Combined totals from across the species's range suggest a decline of 58.6% between 1997-2011 and 2013-2015 (I. Karyakin in litt. 2015). Current Population Trend: Decreasing Habitat and Ecology (see Appendix for additional information) It inhabits areas of steppe and semi-desert, and is recorded breeding up to 2,300 m in mountainous regions (del Hoyo et al. 1994). It feeds mainly on small mammals on its breeding grounds, with susliks forming the vast majority of its diet in some areas; when wintering it appears to feed mainly on mole rats in East Africa, and termites and Red-billed Quelea Quelea quelea predominate in southern Africa (del Hoyo et al. 1994). Nests have traditionally been built as large platforms on the ground, although recent habitat alterations seem to have caused a shift to building a few metres higher in bushes or trees (del Hoyo et al. 1994). It also nests on artificial structures. The species is migratory, with birds wintering in south-east Africa and southern Asia (del Hoyo et al. 1994). Migrants leave their breeding grounds between August and October, returning between January and May (Ferguson-Lees and Christie 2001). It avoids sea crossings and thus forms large concentrations at bottleneck sites (del Hoyo et al. 1994, Snow and Perrins 1998, Ferguson-Lees and Christie 2001). Systems: Terrestrial Threats (see Appendix for additional information) The species has declined in the west of its breeding range, including extirpation from Romania, Moldova and Ukraine, as a result of the conversion of steppes to agricultural land combined with direct persecution (Ferguson-Lees and Christie 2001, Meyburg and Boesman 2013). It is also adversely affected by power lines and is very highly vulnerable to the impacts of potential wind energy developments (Strix 2012, Meyburg and Boesman 2013). It was recently found to be the raptor most frequently electrocuted by power lines in a study in western Kazakhstan (Levin and Kurkin 2013). Young eagles are taken out of © The IUCN Red List of Threatened Species: Aquila nipalensis – published in 2015. http://dx.doi.org/10.2305/IUCN.UK.2015-4.RLTS.T22696038A80351871.en 4 the nest in order to sell them to western European countries (Mebs and Schmidt 2006). A decline in the number of birds and a reduction in the proportion of juveniles migrating over Eilat, Israel began immediately after the Chernobyl nuclear accident in 1986, leading Yosef and Fornadari (2004) to suggest that the species may have been affected by radioactive contamination. This species is vulnerable to the veterinary drug diclofenac (Sharma et al. 2014). Conservation Actions (see Appendix for additional information) Conservation and Research Actions Underway CMS Appendix II. CITES Appendix II. Bern Convention Appendix II. There are currently no conservation actions known to be in place for this species. Conservation and Research Actions Proposed Protect remaining grassland steppes in Europe and the rest of its range. Dangerous electric powerline constructions should be replaced or fitted with protective devices. Educate herdsmen and other locals in the ecological value and vulnerability of this species (Tucker and Heath 1994). Continue research into the impacts of diclofenac and other non-steroidal anti-inflammatory drugs to establish the sensitivity of this species to veterinary drugs. Promote a ban on the use of diclofenac in Europe. Credits Assessor(s): BirdLife International Reviewer(s): Symes, A. Contributor(s): Horvath, M., Karyakin, I., Perlman, Y. & Vyas, V. Facilitators(s) and Compiler(s): Butchart, S., Ekstrom, J., Harding, M., Khwaja, N., Symes, A., Ashpole, J, Wright, L, Pople, R., Burfield, I., Ieronymidou, C. & Wheatley, H. © The IUCN Red List of Threatened Species: Aquila nipalensis – published in 2015. http://dx.doi.org/10.2305/IUCN.UK.2015-4.RLTS.T22696038A80351871.en 5 Bibliography BirdLife International. 2015. European Red List of Birds. Office for Official Publications of the European Communities, Luxembourg. Brazil, M. 2009. Birds of East Asia: eastern China, Taiwan, Korea, Japan, eastern Russia. Christopher Helm, London. del Hoyo, J.; Elliott, A.; Sargatal, J. 1994. Handbook of the Birds of the World, vol. 2: New World Vultures to Guineafowl. Lynx Edicions, Barcelona, Spain. Ferguson-Lees, J. and Christie, D.A. 2001. Raptors of the world. Christopher Helm, London. IUCN. 2015. The IUCN Red List of Threatened Species. Version 2015-4. Available at: www.iucnredlist.org. (Accessed: 19 November 2015). Levin, A. S. and Kurkin, G. A. 2013. The Scope of Death of Eagles on Power Lines in Western Kazakhstan. Raptors Conservation 27(240-244). Mebs, T. and Schmidt, D. 2006. Die Greifvögel Europas, Nordafrikas und Vorderasiens. Kosmos Verlag. Meyburg, B.U. and Boesman, P. 2013. Steppe Eagle (Aquila nipalensis). In: del Hoyo, J., Elliott, A., Sargatal, J., Christie, D.A. and de Juana, E. (eds), Handbook of the Birds of the World Alive, Lynx Edicions, Barcelona. Sharma, A.K., Saini, M., Singh, S.D., Prakash, V., Das, A., Dasan, R.B., Pandey, S., Bohara, D., Galligan, T.H., Green, R.E., Knopp, D. and Cuthbert, R.J. 2014. Diclofenac is toxic to the Steppe Eagle Aquila nipalensis: widening the diversity of raptors threatened by NSAID misuse in South Asia. Bird Conservation International 24: 282-286. Snow, D.W. and Perrins, C.M. 1998. The Birds of the Western Palearctic, Volume 1: Non-Passerines. Oxford University Press, Oxford. STRIX. 2012. Developing and testing the methodology for assessing and mapping the sensitivity of migratory birds to wind energy development. BirdLife International, Cambridge. Tucker, G.M. and Heath, M.F. 1994. Birds in Europe: their conservation status. BirdLife International, Cambridge, U.K. Yosef, R. and Fornasari, L. 2004. Simultaneous decline in Steppe Eagle (Aquila nipalensis) populations and Levant Sparrowhawk (Accipiter brevipes) reproductive success: coincidence or a Chernobyl legacy? Ostrich 75(1&2): 20-24. Citation BirdLife International. 2015. Aquila nipalensis. The IUCN Red List of Threatened Species 2015: e.T22696038A80351871. http://dx.doi.org/10.2305/IUCN.UK.2015-4.RLTS.T22696038A80351871.en Disclaimer To make use of this information, please check the Terms of Use. External Resources © The IUCN Red List of Threatened Species: Aquila nipalensis – published in 2015. http://dx.doi.org/10.2305/IUCN.UK.2015-4.RLTS.T22696038A80351871.en 6 For Images and External Links to Additional Information, please see the Red List website. © The IUCN Red List of Threatened Species: Aquila nipalensis – published in 2015. http://dx.doi.org/10.2305/IUCN.UK.2015-4.RLTS.T22696038A80351871.en 7 Appendix Habitats (http://www.iucnredlist.org/technical-documents/classification-schemes) Habitat Season Suitability Major Importance? 2. Savanna -> 2.1. Savanna - Dry Nonbreeding Suitable Yes 4. Grassland -> 4.4. Grassland - Temperate Breeding Suitable Yes 4. Grassland -> 4.5. Grassland - Subtropical/Tropical Dry Breeding Suitable Yes 4. Grassland -> 4.5. Grassland - Subtropical/Tropical Dry Nonbreeding Suitable Yes 0. Root -> 6. Rocky areas (eg. inland cliffs, mountain peaks) Breeding Suitable No Threats (http://www.iucnredlist.org/technical-documents/classification-schemes) Threat Timing Scope Severity Impact Score 2. Agriculture & aquaculture -> 2.1. Annual & perennial non-timber crops -> 2.1.3. Agro-industry farming Ongoing Majority (5090%) Rapid declines Medium impact: 7 Stresses: 1. Ecosystem stresses -> 1.1. Ecosystem conversion 1. Ecosystem stresses -> 1.2. Ecosystem degradation Ongoing Majority (5090%) Stresses: 1. Ecosystem stresses -> 1.2. Ecosystem degradation 2. Species Stresses -> 2.1. Species mortality Ongoing Majority (5090%) Stresses: 2. Species Stresses -> 2.1. Species mortality Past, unlikely to return Majority (5090%) Stresses: 2. Species Stresses -> 2.3. Indirect species effects -> 2.3.7. Reduced reproductive success Ongoing Majority (5090%) Stresses: 2. Species Stresses -> 2.1. Species mortality Ongoing Minority (50%) Stresses: 2. Species Stresses -> 2.1. Species mortality 2. Species Stresses -> 2.3. Indirect species effects -> 2.3.7. Reduced reproductive success 3. Energy production & mining -> 3.3. Renewable energy 4. Transportation & service corridors -> 4.2. Utility & service lines 5. Biological resource use -> 5.1. Hunting & trapping terrestrial animals -> 5.1.1. Intentional use (species is the target) 9. Pollution -> 9.3. Agricultural & forestry effluents -> 9.3.3. Herbicides and pesticides 12. Other options -> 12.1. Other threat © The IUCN Red List of Threatened Species: Aquila nipalensis – published in 2015. http://dx.doi.org/10.2305/IUCN.UK.2015-4.RLTS.T22696038A80351871.en Slow, significant declines Slow, significant declines Rapid declines Slow, significant declines Slow, significant declines Medium impact: 6 Medium impact: 6 Past impact Medium impact: 6 Low impact: 5 8 Conservation Actions in Place (http://www.iucnredlist.org/technical-documents/classification-schemes) Conservation Actions in Place In-Place Research, Monitoring and Planning Action Recovery plan: No Systematic monitoring scheme: No In-Place Land/Water Protection and Management Conservation sites identified: Yes, over entire range Occur in at least one PA: Yes Invasive species control or prevention: No In-Place Species Management Successfully reintroduced or introduced beningly: No Subject to ex-situ conservation: No In-Place Education Subject to recent education and awareness programmes: No Included in international legislation: Yes Subject to any international management/trade controls: Yes Conservation Actions Needed (http://www.iucnredlist.org/technical-documents/classification-schemes) Conservation Actions Needed 1. Land/water protection -> 1.1. Site/area protection 2. Land/water management -> 2.1. Site/area management 4. Education & awareness -> 4.3. Awareness & communications 5. Law & policy -> 5.1. Legislation -> 5.1.1. International level Research Needed (http://www.iucnredlist.org/technical-documents/classification-schemes) Research Needed 1. Research -> 1.5. Threats Additional Data Fields © The IUCN Red List of Threatened Species: Aquila nipalensis – published in 2015. http://dx.doi.org/10.2305/IUCN.UK.2015-4.RLTS.T22696038A80351871.en 9 Distribution Continuing decline in area of occupancy (AOO): Unknown Extreme fluctuations in area of occupancy (AOO): No Estimated extent of occurrence (EOO) (km²): 6580000 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 Lower elevation limit (m): 0 Upper elevation limit (m): 3000 Population Number of mature individuals: 100000-499999 Continuing decline of mature individuals: Yes Extreme fluctuations: No Population severely fragmented: No Continuing decline in subpopulations: Unknown Extreme fluctuations in subpopulations: No All individuals in one subpopulation: No Habitats and Ecology Continuing decline in area, extent and/or quality of habitat: Unknown Generation Length (years): 16.6 Movement patterns: Full Migrant Congregatory: Congregatory (and dispersive) © The IUCN Red List of Threatened Species: Aquila nipalensis – published in 2015. http://dx.doi.org/10.2305/IUCN.UK.2015-4.RLTS.T22696038A80351871.en 10 The IUCN Red List Partnership The IUCN Red List of Threatened Species™ is produced and managed by the IUCN Global Species Programme, the IUCN Species Survival Commission (SSC) and The IUCN Red List Partnership. 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