This recently described species is only known from one location. It has an extremely small known range, within which it is subject to continuing pressure from agriculture and the development of recreational facilities. It is consequently listed as Critically Endangered.
SACC. 2006. A classification of the bird species of South America. Available at: http://www.museum.lsu.edu/~Remsen/SACCBaseline.html.
Distribution and population
15.5 cm. Strikingly patterned, black, white and red manakin. Male is white with black wings (except for wing-coverts) and tail. Bright crimson red mid-back, nape, crown and frontal tuft of feathers. Reddish iris. Female is olivaceous-green with paler belly and reduced frontal tuft. Voice Quite similar to Helmeted Manakin A. galeata, a musical and warbled uí-guru, guru-uí, guru-uí with variations, and wreee pur calls.
This species was described in 1998 and has been recorded from three municipalities (Crato, Barbalha and Missao Velha), all on the north-eastern slope of the Chapada do Araripe, south Ceará, Brazil
(Coelho and Silva 1998, Aquasis 2006). Surveys conducted in 2005-2006 and 2010 have led to a population estimate of c.800 individuals, which is higher than previously thought (Aquasis 2006, Aquasis in litt.
2011), within a remaining area of suitable habitat estimated at 28 km2
(Aquasis 2006). A total of 46 nests were located in 2004-2007 (Aquasis in litt.
2010). The discovery of the species at a new locality on the top of the Araripe plateau, in January 2012, suggests that its population size and distribution may be slightly greater than previously estimated (Aquasis
In 2006, population size was estimated at 800 individuals based on two consecutive years of auditive censuses. A census at the end of 2010, which visited 93% of the known water springs, represents the most comprehensive survey of the species ever, and resulted in an estimate of 779 individuals, suggesting that the species' population is more or less stable (Aquasis in litt.
2011). It is placed in the band 250-999 individuals to account for uncertainty; this equates to 167-666 mature individuals, rounded here to 150-700 mature individuals.Trend justification
The species is assumed to be declining as an area known to hold seven active nests was burnt in 2004-2005 and the moist forest at springs that the species favours is being cleared to grow crops. Ecology
It inhabits the lower and middle strata of tall, second growth forest (especially where there is an abundance of vines), edge and adjacent clearings, preferring more humid areas of moist forest near springs and streams (Coelho and Silva 1998, J. Mazar Barnett and G. M. Kirwan in litt.
2000). It reportedly feeds on small fruits of Cordia
spp. (Coelho and Silva 1998) and Cecropia
spp., and a recently completed study has already identified 21 other plant species as part of its diet
(Linhares in litt.
2007; Aquasis in litt.
2010). It typically occurs in pairs and breeds in November-April (Aquasis 2006); immature males have been found in March and January
(J. Mazar Barnett and G. M. Kirwan in litt.
2000, J. Minns in litt.
2000). Vocal activity among males is thought to peak between 10h00 and 14h00, and be at its highest during September and October, when rainfall is at its lowest; breeding follows during the wet season when c.76% of tree species bordering gallery forests occupied by Araripe Manakin are fruiting
(Girão and Souto 2005, K. V.
Linhares in litt.
2007). Until recently, all nests discovered had been in vegetation overhanging watercourses (K. V. Linhares in litt.
2007, Linhares et al.
2010), but the recent discovery of a new location in dense forest away from running water suggests this species may not be as reliant on springs and streams as was previously thought (Aquasis 2012). Surveys in 2004-2007 recorded 28 nests in 11 plant species belonging to eight families, most frequently Melastomataceae, Rubiaceae and Piperaceae
(Linhares et al.
2010). Most of the plants used were shrubs (c.36%) or trees (c.46%), although few trees were in their adult phase (Linhares et al.
2010). A clutch of two eggs was observed being incubated solely by the female, while the male vocally defended the territory (Albano and Girão 2009). Threats
Lowlands adjacent to the Chapada have been largely cleared for agriculture (especially banana, maize, beans and tomatoes), cattle raising and the construction of homes (Aquasis 2006). There are several recreational facilities along the slopes of the Chapada do Araripe. These include large open parks and swimming pools, which have involved deforestation in their development, particularly in areas where there is spring water. A large recreational water-park was built at the type-locality in 2000 (Aquasis 2006), but a small patch of habitat is being conserved there, and the species persists despite the disturbance (A. B. Hennessey in litt.
2005). Fires in 2004-2005 largely destroyed an area of forest known to contain seven active nests of the species. Another fire in September 2010 affected the same area, as well as other areas where the species is known to occur (Aquasis in litt.
2010). The springs that supply the streams which support the moist forest habitat of the Araripe Manakin have shown an average reduction of 75% in their outflow over the past hundred years, possibly due to deforestation on the slopes and plateau of the Chapada do Araripe, posing a long-term threat to the manakin's remaining habitat. Diversion, channeling and piping of the springs and streams are also reducing the area of available gallery forest habitat (Aquasis 2006). The species is not known to be trapped either by wildlife traders or by the local population for pets (Aquasis 2006). Conservation Actions Underway
The type-locality is within the Chapada do Araripe Environmental Protection Area, which is adjacent to Araripe National Forest, but both are designated "sustainable use" and consequently fail to prevent exploitation or disturbance of habitat (Aquasis 2006). However, the owner of the land adjacent to the type-locality has decided to protect the remaining forest following the discovery of this species (Coelho and Silva 1998, A. G. Coelho in litt.
1997, J. Mazar Barnett and G. M. Kirwan in litt.
2000). Aquasis (
2012), a local NGO, are in discussions with another landowner concerning the protection of a further 60 ha on the Chapada do Araripe. The Conservation Leadership Programme (CLP) has supported the Conservation of the Araripe Manakin Project in the Chapada do Araripe region since 2004, conducted by Aquasis. In 2007, the project was granted a new award after several years of intensive research into the species's ecological requirements and conservation status, and the development of a conservation plan for the Araripe Manakin; the project team is now focusing on establishing a fully protected area in the Chapada do Araripe that encompasses the remaining moist forest habitat and other areas deemed suitable for habitat restoration (Aquasis 2006, Aquasis in litt.
2010). This process is on-going, and collaborations have been established with several local stakeholders to address various aspects of sustaining long-term conservation actions, including raising awareness and initiating habitat restoration (Aquasis in litt.
2010). Ministry of Environment representatives made a preliminary visit to the site in October 2011 (Aquasis in litt.
2012). The CLP was supporting the Araripe Manakin conservation project again in 2010, with the main objectives of establishing a visitor centre, facilitating and monitoring the process of establishing a fully protected area in the Chapada do Araripe, and encouraging and supporting the formation of local birdwatching groups (Aquasis in litt.
2010). In addition to the local fire service and a specially trained fire brigade that responds to fires in conservation areas, a new fire brigade was being established in the municipality of Crato during 2010 to further increase the response capacity (Aquasis in litt.
2010). The species conservation plan for A. bokermanni
was revised in April 2010, together with ICMBio (a Brazilian environmental organisation), and the federal government is expected to publish a decree recognising its legality (Aquasis in litt.
2010). Aquasis (
2012) is involved in a number of local environmental discussion forums.Conservation Actions Proposed
Survey similar habitats throughout north-east Brazil during September and October between 10h00 and 14h00 when male calling activity is at its peak (Coelho and Silva 1998, Girão and Souto 2005, J. Mazar Barnett and G. M. Kirwan in litt.
2000) to locate additional populations. The most thorough census yet of the species's known population is planned for 2012 (Aquasis in litt.
2012). Formally protect remaining habitat as a national wildlife refuge or national park. Provide incentives for landowners to establish a network of private reseves as a buffer zone (Coelho and Silva 1998). Work with environmental and water management authorities to protect springs and streams along the slopes of the Chapada, and their associated gallery forests (Aquasis 2006). Conduct awareness campaigns in the Araripe region to engender pride in biodiversity and water resources, using the Araripe Manakin as symbol for the conservation of the entire Chapada (Aquasis 2006). Promote and facilitate research on humid forest ecosystem services, as well as species composition and ecology, in order to support future conservation actions related to habitat recovery and restoration (Aquasis 2006, Aquasis in litt.
2010). Minimise or eliminate disturbance and clearance of vegetation along watercourses during the species's nesting season
(Linhares et al.
Related state of the world's birds case studies
Albano, C.; Girão, W. 2009. Araripe Manakin Antilophia bokermanni. Neotropical Birding: 71-74.
AQUASIS. 2006. Aquasis, Fortaleza, Brazil.
AQUASIS. 2012. Araripe Mankin Conservation Project. Aquasis, Caucaia, Brazil.
Coelho, G.; Silva, W. 1998. A new species of Antilophia (Passeriformes: Pipridae) from Chapada do Araripe, Ceará, Brazil. Ararajuba 6(2): 81-84.
Girao, W.; Souto, A. 2005. Breeding period of Araripe Manakin Antilophia bokermanni inferred from vocalisation activity. Cotinga 24: 35-37.
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.
Species Guardian Action Update
Text account compilers
Bird, J., Butchart, S., Mahood, S., Mazar Barnett, J., Pople, R., Sharpe, C J, Symes, A., Taylor, J. & Khwaja, N.
Albano, C., Campos, A., Coelho, A., Girao, W., Hennessey, A., Kirwan, G., Mazar Barnett, J., Minns, J., Mobley, J., Pinto, T. & Linhares, K.
IUCN Red List evaluators
Butchart, S., Symes, A.
BirdLife International (2014) Species factsheet: Antilophia bokermanni. Downloaded from
http://www.birdlife.org on 15/03/2014.
Recommended citation for factsheets for more than one species: BirdLife International (2014) IUCN Red List for birds. Downloaded from
http://www.birdlife.org on 15/03/2014.
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