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Fatuhiva Monarch Pomarea whitneyi
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This species is endemic to one tiny island where, despite its very small population, it was considered secure. However, since the first observation of black rats in 2000 it has declined extremely rapidly and the current population is now estimated to be extremely low. It hence qualifies as Critically Endangered.

Taxonomic source(s)
Sibley, C. G.; Monroe, B. L. 1990. Distribution and taxonomy of birds of the world. Yale University Press, New Haven, USA.

19 cm. Large flycatcher with plush-like feathers on forehead. Adult glossy purplish-black. Immature dull brown above, redder on wings, buffy-white below with rufous tinges to face, neck, and sides of breast. Voice Typical call described as cri-ri-a-rik, similar to the shrill meow of a cat whose tail has been stepped on. Alarm call is a nervous ki ki ki.

Distribution and population
Pomarea whitneyi is endemic to Fatu Hiva in the Marquesas Islands, French Polynesia. In 1975, the population was estimated at several hundred pairs and, in 1990, it was still common (Holyoak and Thibault 1984, Seitre and Seitre 1991). In 2000 the total population was estimated at 400-1,000 individuals (Thibault and Meyer 2001, Gouni 2006). Unlike in 1975, no birds were observed in the groves of mango on the slopes and ridges up the Omoa Valley, and the lack of adults with immatures indicated low breeding success (Thibault and Meyer 2001). Repeat visits in 2003 and 2006 only found the species using three from eight potentially suitable valleys above Omoa, and just one from seven near Hanavave. Furthermore, the encounter rate during surveys declined from 0.35 individuals per point count in 2003 to 0.23 individuals in 2006, a decline of 35% in the number of monarchs detected during that period (Gouni 2006). These catastrophic declines have continued, with a five-month survey in 2009 finding only 0.11 individuals per point count (T. Ghestemme in litt. 2010), and totals of 13 territories and 41 birds found. The total population in 2009 was estimated to be as low as 67 individuals (Le Barh 2009, T. Ghestemme in litt. 2010). In 2011, an estimated 65% of the birds were restricted to a region of 2 km² in the Omoa Valley (Ghestemme et al. 2011).

Population justification
The population was estimated to number 67 individuals in 2009 (T. Ghestemme in litt. 2010). Based on a 30% decline in territories since this estimate, it is now thought to number c. 50 birds, roughly equivalent to 33 mature individuals (T. Ghestemme in litt. 2012).

Trend justification
In February 2000 the total population was estimated at a few hundred pairs (Thibault and Meyer 2001, Gouni 2006), but by 2011 the total population was estimated to have fallen to as low as 50 individuals (Anon. 2010, T. Ghestemme in litt. 2010, 2012). Since the first observation of Black Rats (Rattus rattus) on Fatu Hiva in 2000 there has been an extremely rapid population decline equating to over 90% over 21 years (three generations). Recent predator control has though reduced the rate of territory loss from 60% in 2007-2009, to 30% in 2009-2011 (Ghestemme 2012).

It occurs in dense, native forest from 50 m to 700 m, with some non-breeding birds found up to 775 m on a crest below the highest summit on Mt Touaouoho in native wet forest (Thibault and Meyer 2001). It feeds on insects (e.g. Coleoptera), spiders and seeds (Holyoak and Thibault 1984). Nests are placed in a thin tree fork (Anon. 2010).

Fatu Hiva is a relatively well preserved, well forested island (with no overgrazing or destruction of vegetation by fire). Black Rat (Rattus rattus) was observed for the first time on the island in February 2000 (Thibault and Meyer 2000). Identified as a serious threat as its presence is strongly correlated with the decline and extinction of monarch populations (Thibault et al. 2002), rats already appear to have caused an extremely rapid population decline and represent the principal threat (Gouni 2006). Their density remains very high (T. Ghestemme in litt. 2012). Successful recent breeding has only very rarely been noted except in areas cleared of rats; elsewhere the lack of juveniles indicates a rapidly ageing population, with at least 4 of the 10 protected pairs confirmed as sterile in 2011 (Anon. 2010, Ghestemme et al. 2011). Feral cats also appear to be a significant threat to the species as two adults were sighted without tails, typically a sign of a cat predation attempt. Cats are apparently released in agricultural areas near to where the monarch is found (T. Ghestemme in litt. 2010), and have been found in every part of the island (T. Ghestemme in litt. 2012). They are presumably capable of impacting the monarch even in areas where rats have been cleared (Anon. 2010). Bush fires during the dry season, forest clearance and the establishment of non-regulated agricultural tracks in the species's habitat are also increasing threats (Raust 2010, T. Ghestemme in litt. 2012).

Conservation and Research Actions Underway
The population has been regularly checked since the 1970s (Holyoak and Thibault 1984, Thibault and Meyer 2001). Conservation efforts have increased owing to the recent rapid decline in the population. Rat control has been on-going at accessible territories since 2008. It focuses on the Omoa Valley (T. Ghestemme in litt. 2012), but work is being extended gradually to additional areas (A. Gouni in litt. 2007, T. Ghestemme in litt. 2010): in 2011 all known accessible territories (29 individuals in 12 valleys) were being protected against rats, with significant improvements including spreading bait with catapults to reach previously inaccessible areas (Ghestemme et al. 2011). No nest predation has been recorded in rat controlled areas since January 2010 (T. Ghestemme in litt. 2011). Feral cat control has been underway since August 2010 (Ghestemme et al. 2011). A feasibility study was carried out to assess the suitability of other islands for translocation: without further rat eradications, Rimatara was found to be the only suitable island and due to the small amount of suitable habitat for the Fatuhiva Monarch, translocation of  Tahiti Monarch (P. nigra) was considered preferable here (Ghestemme et al. 2011, A. Gouni in litt. 2007). The island of Makatea has also been assessed as a suitable translocation site if it is eradicated of rats (Albar et al. 2009).  A recovery group, shared with P. nigra, has been established to formulate a conservation strategy (T. Ghestemme in litt. 2010), and a site support group was created in August 2010 (Ghestemme et al. 2011). An awareness campaign is being run, targeted at local people, with an aim to educate about the status of the species, and a poster and t-shirt have been produced as part of the process (T. Ghestemme in litt. 2010). Population banding began in late 2009, with nine birds colour-banded by the end of 2011 (Ghestemme et al. 2011, T. Ghestemme in litt. 2010, 2012). A species action plan is being formulated. The Ministry of Health and Environment is working to reduce bushfires during times of drought and increasing regulation of agricultural tracks that would impact the species's habitat (Raust 2010).

Conservation and Research Actions Proposed
Continue and improve rat control in areas where this work is already ongoing, and expand control to other areas (Thibault and Meyer 2000, Thibault et al. 2002, T. Ghestemme in litt. 2010). Examine the feasibility of complete rat eradication. Produce a more detailed action plan (T. Ghestemme in litt. 2012). Conduct surveys elsewhere on the island using the same methodologies and continue to monitor the known population through banding (Gouni 2006, T. Ghestemme in litt. 2010). Consider translocation, either to another island or by creating another, larger controlled area in an accessible part of Fatu Hiva which would allow birds to be translocated to it from valleys where protection is impossible (Anon. 2010). Establish a captive-breeding programme to aid in establishment of new populations/supplementing existing populations.  Continue the public awareness programme (Gouni 2006, T. Ghestemme in litt. 2010). Continue and extend cat control and assess its effect on the species (T. Ghestemme in litt. 2010).

Albar, G., Gouni, A., Kesler, D., Autai, T., Serra, C. and Faulquier, L. 2009. Etude de l'avifaune endémique de l'île de Makatea (archipel des Tuamotu, Polynésie française). Rapport non publié. Société d'Ornithologie de Polynésie, Tahiti, Polynésie française.

Anon. 2010. Catastrophic decline of the Fatu Hiva Monarch forces increased conservation measures. BirdLife International Pacific Partnership e-Bulletin: 2.

Collar, N. J.; Butchart, S. H. M. 2013. Conservation breeding and avian diversity: chances and challenges. International Zoo Yearbook.

Ghestemme, T. 2012. Le monarque de Fatu Hiva menacé de disparition. L'Oiseau 105: 24-25.

Gouni, A. 2006. Bilan mitigé pour le programme de sauvegarde du Monarque de Fatu Hiva en 2006. Te Manu: 5-6.

Holyoak, D. T.; Thibault, J. -C. 1984. Contribution à l'étude des oiseaux de Polynésie orientale. Memoires du Museum National d'Histoire Naturelle - Serie A: Zoologie 127: 1-209.

IUCN. 2015. The IUCN Red List of Threatened Species. Version 2015-4. Available at: (Accessed: 19 November 2015).

Raust, P. 2010. Nouvelles menaces sur le Monarque de Fatu Hiva. Te Manu: 5-6.

Seitre, R.; Seitre, J. 1991. Causes de disparition des oiseaux terrestres de Polynésie Française. South Pacific Regional Environment Programme, Nouméa.

Thibault, J. C.; Martin, J. L.; Penloup, A.; Meyer, J. Y. 2002. Understanding the decline and extinction of monarchs (Aves) in Polynesian Islands. Biological Conservation 108: 161-174.

Thibault, J.-C.; Meyer, J.-Y. 2000. The arrival of the black rat (Rattus rattus) on Fatuiva, Marquesas Islands. Bulletin de la Société d'Ornithologie de Polynésie (Te Manu) 31: 5-7.

Thibault, J.-C.; Meyer, J.-Y. 2001. Contemporary extinction and population declines of the monarchs (Pomarea spp.) in French Polynesia, South Pacific. Oryx 35: 73-80.

Further web sources of information
Alliance for Zero Extinction (AZE) species/site profile. This species has been identified as an AZE trigger due to its IUCN Red List status and limited range.

Click here for more information about the Alliance for Zero Extinction (AZE)

Explore HBW Alive for further information on this species

Search for photos and videos, and hear sounds of this species from the Internet Bird Collection

Species Guardian Action Update

Text account compilers
Bird, J., Calvert, R., Derhé, M., O'Brien, A., Shutes, S., Stattersfield, A., Symes, A., Khwaja, N. & Wright, L

Ghestemme, T., Gouni, A. & Raust, P.

IUCN Red List evaluators
Symes, A.

Recommended citation
BirdLife International (2016) Species factsheet: Pomarea whitneyi. Downloaded from on 22/10/2016. Recommended citation for factsheets for more than one species: BirdLife International (2016) IUCN Red List for birds. Downloaded from on 22/10/2016.

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.

Key facts
Current IUCN Red List category Critically Endangered
Family Monarchidae (Monarchs)
Species name author Murphy & Mathews, 1928
Population size 33 mature individuals
Population trend Decreasing
Distribution size (breeding/resident) 80 km2
Country endemic? Yes
Links to further information
- Additional Information on this species