email a friend
printable version
Northern Bald Ibis Geronticus eremita
BirdLife Species Champion HSH Prince Albert II of Monaco
BirdLife Species Guardian General Commission for Al Badia Management and Development (Syria)
For information about BirdLife Species Champions and Species Guardians visit the BirdLife Preventing Extinctions Programme.

This species has undergone a long-term decline and now has an extremely small population, with over 95% of truly wild birds concentrated in one subpopulation in Morocco. Numbers are currently increasing owing to management actions and consequent improved breeding success. However, this improvement in its status in Morocco is very recent and has not yet led to an increase in the number of colonies. In Syria its population appears to have declined dramatically in the past 30 years. The species is precautionarily retained as Critically Endangered for these reasons.

Taxonomic source(s)
AERC TAC. 2003. AERC TAC Checklist of bird taxa occurring in Western Palearctic region, 15th Draft. Available at: # _the_WP15.xls#.
Cramp, S.; Perrins, C. M. 1977-1994. Handbook of the birds of Europe, the Middle East and Africa. The birds of the western Palearctic. Oxford University Press, Oxford.
del Hoyo, J.; Collar, N. J.; Christie, D. A.; Elliott, A.; Fishpool, L. D. C. 2014. HBW and BirdLife International Illustrated Checklist of the Birds of the World. Barcelona, Spain and Cambridge UK: Lynx Edicions and BirdLife International.

70-80 cm. Large ibis. Black overall, with iridescent tints of blue, green and copper in sunlight. Red, naked face and crown. Long, narrow feathers project from nuchal area to form ruff. Voice Usually silent. Various hisses and grunts at nest and in display.

Distribution and population
The historical range of Geronticus eremita probably extended throughout North Africa and into the Middle East. Since the beginning of the 20th century, however, the species has been known from two disjunct populations: a western population in Morocco and an eastern population in Turkey and Syria. In Morocco it is found at Souss-Massa National Park (Souss-Massa NP) (338 km2; three sub-colonies) and at nearby Tamri (one colony, half the breeding population) (Bowden 1998), with some movement of birds between these two. In 1995, the Moroccan population was estimated at 300 individuals (74 breeding pairs that laid eggs) (Bowden et al. 2003). In 1998, it had declined to 59 pairs, following the mysterious death of 40 birds in 1996 (Bowden 1998, Touti et al. 1999), but by 2006 there were 95 pairs that laid eggs (El Bekkay and Oubrou 2004). Importantly, since 1980 there has been no overall decline in numbers at Souss-Massa NP (Bowden et al. 2003). At present the population in Morocco is stable and productivity is good with 148 young fledged in 2013, and a total population at the end of the breeding season of 443 individuals (SEO/BirdLife Morocco 2013). There is some cause for optimism that former areas may soon be recolonised (C. Bowden in litt. 2006).

The eastern population was believed to have died out, however, in 2002, a tiny colony, consisting of just seven individuals, was rediscovered at Palmyra in Syria (Serra et al. 2003). Having barely rediscovered this population it now looks as though it will once more be lost, with just a single individual returning to the colony in 2013 (C. Bowden in litt. 2013). Being migratory, the Syrian population is behaviourally distinct from the Moroccan one, with which it is thought to have separated long ago. During the six breeding seasons following the rediscovery (2002-2007), the three, and then two, pairs breed well and a total of 24 chicks fledged and left the breeding area successfully (Serra et al. 2009).Between 2004 and 2007, five immature ibises returned to the colony (Serra et al. 2009). In 2008, breeding failed with four chicks dying, probably due to predation by Brown-necked Raven Corvus ruficollis (Hirschfeld 2008). The causes of failed breeding in 2009 are uncertain, but intraspecific disturbance and low spring rainfall are possible factors (Murdoch 2010). In 2011, a single breeding pair fledged two young (R. Grimmett in litt. 2011), but the same pair failed to breed in 2012 (C. Bowden in litt. 2012). Searches in 2003 for further colonies within the Syrian steppes proved fruitless (Serra et al. 2003, Serra et al. 2004).

Satellite-tagging has revealed that this population migrates south through Jordan and Saudi Arabia; six birds spent three weeks in Yemen (July-August), then wintering in central Ethiopia; migrating back to Syria, through Eritrea, Sudan, Saudi Arabia and Jordan in February (Lindsell et al. 2009); four adults were located in Ethiopia in the winters of 2006-07, 2007-08, 2008-09 and January 2013 (Serra and Wondafrash 2009, SEO/BirdLife Morocco 2013). Records of untagged birds in Israel and Djibouti in late 2007 may relate to immature birds from the Syrian colony or birds from an as yet undiscovered population (Hirschfeld 2008). A semi-wild population numbering 91 individuals in 2006 exists at Birecik, Turkey (J. Tavares in litt. 2007), where birds are free-flying for five months, breeding on natural nest sites and nest-boxes on cliffs, but are taken into captivity after the breeding season to prevent them from migrating (G. Eken in litt. 2005, J. Tavares in litt. 2007). Three birds from the colony migrated in 2009 travelling via the Palmyra site. However, three were found dead in Jordan (Niemann 2009). In 2013 six individuals have been selected to remain in the wild and at least five of these have migrated south stopping very close to the Palmyra site (C. Bowden in litt. 2013). Historically, the species occurred across parts of southern Europe, and captive populations have been maintained in Austria (at Grünau, 22 birds, now breeding) and Spain, with a long-term aim to re-establish the species in parts of its former range. Around 30 birds have now been released in the La Janda area, Spain, and in 2008 a released pair laid two eggs, perhaps the first breeding of the species in the wild in Spain for 500 years (Hirschfeld 2008).

Population justification
In Souss-Massa National Park and Tamri, Morocco, 113 pairs (i.e. 226 mature individuals) nested, out of 319 adults in 2013, and produced 148 fledged young (Oubrou and El Bekkay 2013). In 2011, at least 100 pairs produced at least 130 fledged young, matching the breeding success of 2010, when 105 pairs fledged 138 young (R. Grimmett in litt. 2011). After the breeding season the total number of birds in the western population may have exceeded 500 in 2011-2012 (IAGNBI 2012), but most recently has been evaluated as 443 individuals (SEO/BirdLife Morocco 2013). Only a single mature female returned to Syria in 2013 (C. Bowden in litt. 2013), and 2011 was the last successful breeding when a single breeding pair fledged two young (R. Grimmett in litt. 2011). The Turkish population now numbers around 100 individuals (IAGNBI 2012), but these managed birds are excluded from the total estimate.

Trend justification
An unquantified decline is indirectly estimated to have occurred over the last three generations. The Moroccan population has been stable since 1980, however Serra (2003) provides reasonable evidence, including testimonies of local people, that in Syria the species was still common 20 years ago and possibly quite abundant 30 years ago. Colonies of several hundred probably existed up until 1980. Although the Turkish population may be now recovering to levels it was at ten or more years ago, this heavily managed population is excluded from the overall trends.

Behaviour The small Syrian population is migratory, but the larger western population is dispersive (del Hoyo et al. 1992). Breeding occurs in colonies of up to 40 pairs, beginning in mid-February, and eggs are laid in March-April (del Hoyo et al. 1992). Colonies are vacated in late June or early July, but migration and dispersal do not commence until August, with birds recorded on the breeding grounds as late as November (Cramp et al. 1977). Some reside in Souss-Massa NP and around Tamri throughout the year (Bowden et al. 2003). Juveniles tend to disperse over the longest distances (del Hoyo et al. 1992). Movements appear to be to some extent determined by rainfall (Hancock et al. 1992). Migrating birds from the Syrian population do not arrive in their Ethiopian winter quarters before December (Cramp et al. 1977). All return to their breeding colonies in February and March (Cramp et al. 1977). Birds in general are gregarious throughout the year (Brown et al. 1982). The species forages in loose groups with birds well spread out (Cramp et al. 1977), but commutes in flocks between the colony or roost and the feeding grounds (Cramp et al. 1977). Winter flocks vary from a few individuals to over 100 (Cramp et al. 1977). Breeding performance is highly variable from one year to the next (Bowden et al. 2003), but does not appear to be related to rainfall in the vicinity of the colonies as previously reported elsewhere. It is suggested that coastal fogs in the Souss-Massa region may buffer the adverse impacts of low rainfall, and may in part account for the year-round residency of the birds (Bowden et al. 2003).

Breeding Colonies are usually situated in rocky areas, cliffs and escarpments in remote arid regions (Cramp et al. 1977). In the past castles, ruins and walls were used as nest sites even in urban areas (Hancock et al. 1992). They are often located near the banks of rivers, along streams or on the coast (Hancock et al. 1992). Birds may feed on dry ground and rocky slopes, as well as in wetlands, on coastal sandy strips, on river beds and in sandy banks on the sea shore (Hancock et al. 1992). Roosts away from the breeding site can be in trees, on cliff ledges or sometimes in fields (Hancock et al. 1992). Non-breeding During the non-breeding season it may be found in mountain meadows, stubble fields, short grass, rocky semi-arid ground, and damp ground in lower areas of high plateaus (Hancock et al. 1992). It prefers areas with very sparse vegetation, but sometimes frequents pastures and cultivated fields (Aghnaj et al. 2001). It avoids tilled fields and pastures where the grass exceeds 25 cm in height (Hancock et al. 1992). Birds that migrate to Ethiopia during the non-breeding season feed on high moors, wet meadows and by fast-flowing mountain streams and lake margins up to 3,500 m elevation (Hancock et al. 1992). Diet It has a broad diet, feeding on any available animal life (Aghnaj et al. 2001) including insects, arachnids, scorpions, earthworms, snails and vertebrates such as fish, amphibians, lizards and snakes, small rodents and small birds, whether alive or dead (Hancock et al. 1992). It will also feed on vegetation including berries, shoots, duckweed, and rhizomes of aquatic plants (Hancock et al. 1992).

It has declined for several centuries, perhaps partly owing to unidentified natural causes. However, the more recent rapid decline is undoubtedly the result of a combination of factors, with different threats affecting different populations. In Morocco, illegal building and disturbance close to the breeding cliffs and changes in farming on the feeding grounds are the threats that may have the most severe impact on the population. Hunting is the main threat to the tiny Syrian population, and overgrazing and collecting of firewood have reduced habitat quality in feeding areas. A well was under construction at a main feeding site in Syria in 2007. This is likely to increase disturbance to the species and might render this important site unsuitable in the near future (G. Serra in litt. 2007). Disturbance from other human activities is on-going, and this population is also potentially threatened by trophy hunters, combined with a lack of safe areas with water sources (Serra et al. 2009). The integrity of the protected area at the Syrian breeding colonies is potentially threatened by oil concessions, infrastructure development and plans for urbanisation (Serra et al. 2009, Murdoch 2010). Satellite tracking of juvenile birds indicates that the main threat to the eastern population is mortality from hunting in the Arabian Peninsula. Three birds tagged in summer 2010 did not survive their first winter (R. Grimmett in litt. 2011). Breeding productivity in Syria in 2005 was zero: local rangers reported predation as the cause. In Turkey, a major historical threat was poisoning and reduced breeding success caused by pesticides used against locusts and mosquitoes (Murdoch 2010). In Syria, the most serious nest predator is Brown-necked Raven Corvus ruficollis, however, predation by Egyptian Vulture Neophron percnopterus on young ibis chicks is also suspected (Serra et al. 2009). The Birecik population has also suffered from losses to predation in some years (J. Tavares pers. comm. 2008). At Souss-Massa NP, the most recent causes of breeding failure have been loss of eggs to predators and, more importantly, poor chick survival as a result of starvation and predation (Bowden et al. 2003). A proposed tourist development at the national park could prove detrimental to the birds if it is not constructed in a sensitive way (Anon 2009). Poisoning was suspected to be the cause of death of three tagged individuals found in Jordan, however electrocution whilst standing on electricity pylons is now believed to have been the most likely cause (Anon 2009).

Conservation Actions Underway
CITES Appendix I. CMS Appendix I and II. In 1999, an international advisory group IAGNBI was created to coordinate efforts and provide scientific advice (Bowden 2001). An international species action plan was published in 2006. Over 1,000 individuals of the western population exist in captivity worldwide, but birds from the eastern population are much rarer in captivity (four Turkish zoos hold 20 birds and participate in an ex situ breeding operation (Böhm 2004)). An international studbook was discontinued in 1998 (Böhm 2004). An in situ breeding programme at Birecik aims to establish a partially captive population of 150 birds to provide birds for release to the wild population if this action is agreed in future (Böhm 2004). Colour-ringing of young at Birecik has begun and there are plans to attach satellite transmitters to a family party in July 2007 (J. Tavares in litt. 2007). A captive breeding centre has been built at Ain Tijja-Mezguitem, northeastern Morocco, and is stocked with zoo-bred birds imported in 2000 and 2004 (WAZA In 2004, an information centre was also constructed. Six pairs bred in 2006 and successfully reared six offspring. In 2007, the aviary contained 19 birds (13 adults and six juveniles). A reintroduction is planned once the population has reached around 40 birds (WAZA Other captive breeding schemes exist or are planned in Austria, Spain and Italy, and programmes of releasing captive birds are either in progress or in the experimental phase in Bavaria, Spain, and Italy (N. Schaffer in litt. 2007, UNEP/CMS 2008, Fritz 2010). In southern Spain a total of 109 birds were released between 2004 and 2007. Although juvenile mortality has been high, the first breeding pair was formed on nearby cliffs in 2008. Further releases were planned for late 2008, and the organisers hoped the project would be continued until 2010 (Quevedo and Sánchez 2009). There have been experimental field studies of the feeding ecology of hand-raised individuals in potential summer and winter habitat in Europe (Zoufal et al. 2006).

In 1991, the Souss-Massa National Park was designated specifically to protect nesting and feeding areas (Bowden et al. 2003) and in 1994, a monitoring and research programme was set up involving local people (Bowden 1998). The provision of freshwater near the breeding colonies in the national park has been shown experimentally to increase productivity, buffering individuals against the impacts of low rainfall, and is now an ongoing conservation measure (Smith et al. 2008). The Palmyra project in Syria has initiated a research and protection programme in collaboration with local communities. Three birds were satellite-tagged there in June 2006 (Anon. 2006), and one in 2007; giving an indication of the migratory route of Syrian individuals. Syria's first local conservation society, the Palmyra Society for the Protection of Environment and Wildlife, aims to develop ecotourism in the area (Anon. 2008). The breeding area in Syria was declared a protected area in 2004 by Ministry of Agriculture and Agrarian Reform. It was also declared as an IBA by BirdLife in 2007. Ecotourism and awareness raising has been promoted throughout the range. Conservation action to date has focused on reducing the negative influences on breeding success, but it is recognised that for such a long-lived bird adult survival is also likely to be an important limiting factor on the population size. Plans to release young birds from the Birecik colony in Syria during 2009 were halted by delays in obtaining permissions from the Turkish authorities, although it was hoped that this would be possible in 2010 (Anon. 2008). Conservation Actions Proposed
Conduct research into feeding and breeding biology, and habitat requirements (Brindley et al. 1995). Continue to monitor numbers and breeding success (Bowden et al. 2003). Study threats along the migration route and in the non-breeding range of the Syrian population (Anon. 2008). Protect key breeding and roosting sites from disturbance and development (Bowden et al. 2003), making sure to involve local people (Serra et al. 2009). Better demarcation and stricter enforcement is needed at the Syrian breeding site (Serra et al. 2009). Employ management techniques such as the provision of drinking water (Serra et al. 2009). Raven populations around breeding sites should be controlled (Serra et al. 2009). Explore the possibility of reintroducing captive-bred birds into previously occupied sites (when detailed information on ecological requirements is available) (Brindley et al. 1995, Mendelssohn 1994, Bowden 2001). Research feasibility of re-establishing wild (preferably migratory) population in Turkey (J. Tavares in litt. 2007). Better link the Birecik and Syrian populations and projects; research potential to supplement Syrian colony with birds from Turkey (J. Tavares in litt. 2007, Serra et al. 2009). Continue with current husbandry at Birecik to increase colony to 150-200 birds (J. Tavares in litt. 2007). Protect wintering areas in Ethiopia. Raise awareness among hunters on the migration route (Anon. 2006). In Syria, address issues over land tenure and encourage the rehabilitation of pastures (Serra et al. 2009). Develop a national action plan for the Syrian population (Serra et al. 2009).

Related state of the world's birds case studies

Aghnaj, A.; Smith, K. W.; Bowden, C. G. R.; Ribi, M. 2001. Studies of the feeding ecology and habitat use of Northern Bald Ibis, Geronticus eremita, in the Souss-Massa National Park, Morocco. Ostrich Suppl. 15: 197.

Anon. 1998. Recent reports. Bulletin of the African Bird Club 5(1): 71-72.

Anon. 2006. Bald Ibises tagged in Syria. Birding World 19(7): 308.

Anon. 2008. Poison blamed for Bald Ibis deaths. World Birdwatch 30(4): 10.

Anon. 2009. Bald Ibises - update. RSPB Legal Eagle: 16.

Böhm, C. 2004. Waldrapp ibis (Geronticus eremita).

BirdLife International. 2009. First coordinated White-shouldered Ibis count dramatically increases known population. Babbler: 22-23.

Bowden, C. 1998. Birecik: the current situation of the semi-wild Bald Ibis Geronticus eremita population.

Bowden, C. 2001. An update on current projects involving wild and captive Northern Bald Ibis Geronticus eremita. International Advisory Group for Northern Bald Ibis Newsletter.

Bowden, C. G. R.; Aghnaj, A.; Smith, K. W.; Ribi, M. 2003. The status and recent breeding performance of the critically endangered Northern Bald Ibis Geronticus eremita population on the Atlantic coast of Morocco. Ibis 145: 419-431.

Brindley, E.; Dimmick, C.; Bowden, C.; Ribi, M.; Hoffmann, D.; del Nevo, A. 1995. The Bald Ibis: a species on the brink? RSPB Conservation Review 9: 76-79.

Brown, L. H.; Urban, E. K.; Newman, K. 1982. The birds of Africa vol I. Academic Press, London.

Collar, N. J.; Stuart, S. N. 1985. Threatened birds of Africa and related islands: the ICBP/IUCN Red Data Book. International Council for Bird Preservation, and International Union for Conservation of Nature and Natural Resources, Cambridge, U.K.

Cramp, S.; Simmons, K. E. L. 1977. Handbook of the birds of Europe, the Middle East and Africa. The birds of the western Palearctic, vol. I: ostriches to ducks. Oxford University Press, Oxford.

del Hoyo, J.; Elliot, A.; Sargatal, J. 1992. Handbook of the Birds of the World, vol. 1: Ostrich to Ducks. Lynx Edicions, Barcelona, Spain.

El Bekkay, M.; Oubrou, W. 2004. The Bald ibis in Souss Massa Region (Morocco). International Advisory Group for Northern Bald Ibis Newsletter: 30-32.

Hancock, J. A.; Kushlan, J. A.; Kahl, M. P. 1992. Storks, ibises and spoonbills of the world. Academic Press, London.

Hirschfeld, E. 2008. Rare Birds Yearbook 2009: the world's 190 most threatened birds. MagDig Media Ltd., Shrewsbury, UK.

IAGNBI. 2012. International Advisory Group for the Northern Bald Ibis website. Available at:

Jimenez Armesto, M. J.; Boehm, C.; Bowden, C. 2006. International single species action plan for the conservation of the Northern Bald Ibis Geronticus eremita. AEWA, Bonn, Germany.

Lindsell, J. A.; Serra, G.; Peske, L.; Abdullah, M. S.; Qaim, G. al; Kanani, A.; Wondafrash, M. 2009. Satellite tracking reveals the migration route and wintering area of the Middle East population of Critically Endangered Northern Bald Ibis Geronticus eremita. Oryx 43(3): 329-335.

Mendelssohn, H. 1994. Experimental releases of Waldrapp Ibis Geronticus eremita: an unsuccessful trial. International Zoo Yearbook 33: 79-85.

Niemann, S. 2009. Poisoned ibises. Birds 22(5): 25.

Oubrou, W. and El Bekkay, M. 2013. Rapport sur la reproduction 2013 de la population des Ibis chauves dans la région de Souss-Massa. Report of the 2013 Northern Bald Ibis breeding season at Sous-Massa NP, Morocco. Available at: (Accessed: 07/10/2013).

Pegoraro, K.; Föger, M.; Parson, W. 2001. First evidence of DNA sequence differences between Northern Bald Ibises (Geronticus eremita) of Moroccan and Turkish origin. Journal für Ornithologie 142: 425-428.

Quevedo, M. A.; Sánchez, I. 2009. The bald facts. EAZA News: 12-14.

Serra, G. and Wondafrash, M. 2009. Eco-ethological and conservation survey of N. Bald Ibises wintering in the Northern Shawa (Ethiopia) during 2008-09. EWNHS/IUCN report.

Serra, G.; Abdallah, M.; Assaed, A.; Abdallah, A.; Al Qiam, G.; Fayad, T.; Williamson, D. 2004. Discovery of a relict breeding colony of Northern Bald Ibis Geronticus eremita in Syria. Oryx 38: 106-108.

Smith, K. W.; Aghnaj, A.; El Bekkay, M.; Oubrou, W.; Ribi, M.; Jimenez Armesto, M.; Bowden, C. G. R. 2008. The provision of supplementary fresh water improves the breeding success of the globally threatened Northern Bald Ibis Geronticus eremita. Ibis 150(4): 728-734.

Touti, J.; Oumellouk, F.; Bowden, C. G. R.; Kirkwood, J. K.; Smith, K. W. 1999. Mortality incident in Northern Bald Ibis Geronticus eremita in Morocco in May 1996. Oryx 33: 160-167.

UNEP/CMS. 2008. Northern Bald Ibis (Geronticus eremita). In: Vagg, R. (ed.), CMS Family Guide: the encyclopaedia of the Convention on the Conservation of Migratory Species of Wild Animals, pp. Species 22. UNEP-CMS Secretariat, Bonn, Germany.

Zoufal, K.; Fritz, J.; Bichler, M.; Kirbauer, M.; Markut, T.; Meran, I.; Riedler, B. 2006. Feeding ecology of the Northern Bald Ibis in its European winter and summer habitat: an experimental field study with hand-raised individuals. Journal of Ornithology 147(5): 279.

Further web sources of information
Detailed regional assessment and species account from the European Red List of Birds (BirdLife International, 2015)

African-Eurasian Waterbird Agreement (AEWA) International Action Plan 2006

Detailed species account from Birds in Europe: population estimates, trends and conservation status (BirdLife International 2004)

Explore HBW Alive for further information on this species

RSPB - Ecology of threatened species

RSPB - International Research - Northern Bald Ibis

Species Guardian Action Update

View photos and videos and hear sounds of this species from the Internet Bird Collection

Text account compilers
Benstead, P., Bird, J., Butchart, S., Calvert, R., Ekstrom, J., Pilgrim, J., Pople, R., Shutes, S., Taylor, J., Allinson, T, Symes, A., Khwaja, N., Martin, R

Bowden, C., Buckley, P., Eken, G., Engin, G., Heip, C., Schäffer, N., Sekercioglu, C., Serra, G., Tavares, J.

Recommended citation
BirdLife International (2015) Species factsheet: Geronticus eremita. Downloaded from on 09/10/2015. Recommended citation for factsheets for more than one species: BirdLife International (2015) IUCN Red List for birds. Downloaded from on 09/10/2015.

This information is based upon, and updates, the information published in BirdLife International (2000) Threatened birds of the world. Barcelona and Cambridge, UK: Lynx Edicions and BirdLife International, BirdLife International (2004) Threatened birds of the world 2004 CD-ROM and BirdLife International (2008) Threatened birds of the world 2008 CD-ROM. These sources provide the information for species accounts for the birds on the IUCN Red List.

To provide new information to update this factsheet or to correct any errors, please email BirdLife

To contribute to discussions on the evaluation of the IUCN Red List status of Globally Threatened Birds, please visit BirdLife's Globally Threatened Bird Forums.

Additional resources for this species

ARKive species - Northern bald ibis (Geronticus eremita) 0

Key facts
Current IUCN Red List category Critically Endangered
Family Threskiornithidae (Ibises, Spoonbills)
Species name author (Linnaeus, 1758)
Population size 200-249 mature individuals
Population trend Decreasing
Distribution size (breeding/resident) 590 km2
Country endemic? No
Links to further information
- Additional Information on this species
- 2015 European Red List assessment