Chamek Spider Monkey - Ateles chamek
( Humboldt, 1812 )

 

 

No Map Available

Warning: Undefined property: stdClass::$Photo1 in /var/www/vhosts/virtualzoo/classifications/display.php on line 584
No Photo Available No Map Available

Subspecies: Unknown
Est. World Population:

CITES Status: NOT LISTED
IUCN Status: Endangered
U.S. ESA Status: NOT LISTED

Body Length:
Tail Length:
Shoulder Height:
Weight:

Top Speed:
Jumping Ability: (Horizontal)

Life Span: in the Wild
Life Span: in Captivity

Sexual Maturity: (Females)
Sexual Maturity: (Males)
Litter Size:
Gestation Period:

Habitat:
The species occurs in lowland terra firme unflooded forest, semi-deciduous forest, riparian and flooded forest (várzea and igapó forests) with little or no hunting pressure (van Roosmalen and Klein 1988; Konstant and Rylands 2013). They are also found in transitional forest (forest to savanna) in southwestern Amazonia. In Bolivia, in the Noel Kempff Mercado National Park, Wallace et al. (1998) recorded A. chamek most often in tall forest (4.42 encounters per 10 km), followed by so-called saternejal forest (along the forest–savanna border, in the vicinity of small forest streams that undergo periodic flash floods; 2.49 encounters per 10 km). Garcia and Tarifa (1988) found A. chamek to be restricted to high forest in the Beni Biological Station. Otherwise, Alves (2013) recorded A. chamek in both unflooded terra firme and open/dense igapó clear-water flooded forests, but not in cerradão dense savanna woodland. This taxon is restricted to primary forest. The population decline and local extinction of Ateles in most areas with human activity are the result of hunting pressure that is often associated with habitat destruction and degradation (van Roosmalen and Klein 1988; Peres 1997; Parry et al. 2007). The species of the genus are present in altered/fragmented areas but generally do not persist for long periods (Peres 1990, 1997). In the state of Rondônia (Brazil), A. chamek occurs in some forest fragments without hunting pressure (Ferrari et al. 1996; Iwanaga and Ferrari 2001, 2002), indicating a relative flexibility of the taxon to habitat disturbances in the absence of hunting.

Spider monkeys travel and forage in the upper levels of the forest. They spend most time in the upper canopy, sometimes using the middle and lower strata but are rarely seen in the understory. Due to the use of the highest levels of the forest, they spend more time hanging from branches, moving by brachiation, arm swinging, and climbing, than walking or running on all fours. They are highly frugivorous and feed largely on the mature, soft parts of a very wide variety of fruits, which comprise about 80-90% of their diet and are found mainly in the emergent trees and upper part of the forest canopy (van Roosmalen and Klein 1988). In the state of Rondônia (Brazil), Iwanaga and Ferrari (2001) recorded a diet consisting of 97.1% fruits, of which the Moraceae and Caesalpinaceae families account for 53.3% of the species exploited by A. chamek. Similar findings were presented by Felton et al. (2008) for the Guarayos Forest Reserve in Bolivia, where Moraceae was the most important plant family in the diet, both in terms of number of species and time spent feeding. They also eat young leaves and flowers (especially during periods of fruit shortage at the beginning of the dry season), but occasionally also young seeds, floral buds, pseudobulbs, aerial roots, bark, decaying wood, honey, and at rare occasions small insects such as termites and caterpillars. They play a significant role as seed dispersers. Van Roosmalen (1985) and van Roosmalen and Klein (1988) found that A. paniscus was dispersing the seeds of at least 138 species (93.5% of all fruits species consumed) through their ingestion and subsequent defecation (endozoochory). Another 10 species were dispersed by carrying them off some distance from the tree before dropping them (exozoochory). Only in 23 species the seeds were ruined or digested (seed predation).

Spider monkeys live in large, territorial, multi-male/multi-female groups of 37-55 individuals (Wallace 2005; Konstant and Rylands 2013). However, they are rarely seen together, and almost always found travelling, feeding and resting in subgroups of varying size and composition (usually 2-4 individuals). The only persistent association is that of a mother and her offspring (McFarland Symington 1990). Iwanaga and Ferrari (2002) recorded a mean (± SE) group size of 3.34 ± 2.60 individuals (n = 219 sightings) at a number of localities in the state of Rondônia in Brazil. At Lago Uauaçú, in the lower Rio Purús region, Haugaasen and Peres (2005) observed a mean groups size of 6.0 individuals/group in terra firme forest, but 12.6 individuals/group in várzea forest. Often single group members travel on their own, and each female occupies a preferred “core area” within the group’s home range. Klein and Klein (1976, 1977) estimated 259-388 ha home ranges with 20-30% overlap between groups for A. belzebuth in La Macarena National Park in Colombia. Ateles species are rarely seen in association with other primates, and if, they are occasional and ephemeral, resulting from the simultaneous occupation of fruiting trees.

Six estimated birth periods, spread throughout the year, were given by Klein (1971) for Ateles belzebuth (i.e., December, January, April, September, October and November). Spider monkeys apparently reach sexual maturity at 4-5 years of age (Klein 1971; Eisenberg 1973, 1976). They give birth to a single offspring after a long gestation period of 226-232 days, with a minimum birth interval of 17.5 months (in captivity) or 28-30 months in the wild (Eisenberg 1973, 1976). Late maturation and long inter-birth intervals make it difficult for the species to recover from hunting and other threats.

Range:

Black-faced Black Spider Monkey is found in the northern and central lowlands of Bolivia, western Brazil and north-eastern Peru. It occurs to the South of the Rio Amazonas-Solimões, west of the Rios Tapajós-Teles and Pires, to the Río Ucayali in Peru (where it is replaced by Ateles belzebuth on the left bank of the lower Ucayali). It crosses the middle Ucayali south of the Río Cushabatay (a left bank tributary of the Ucayali), extending into the interfluvium of the Ríos Ucayali and Huallaga (Konstant and Rylands 2013). From there, it extends south along the eastern Cordillera into Bolivia, south of the Río Madre de Dios, south to about 17ºS, and from there extending north-east through the Noel Kempff Mercado National Park (Wallace et al. 1998), into the states of Rondônia and Mato Grosso, Brazil, to the left bank of the Rio Teles Pires and Rio Tapajós. Rabelo et al. (2014) recorded the species in the Mamirauá Sustainable Development Reserve (Amazonas, Brazil), on the northern bank of the Rio Solimões, extending the known distribution of Ateles chamek to the interfluvium of the Rios Solimões and Japurá.


Conservation:

This species is confirmed, or may occur, in a number of protected areas:

Bolivia

  • Manuripi Heath National Park (1,884,000 ha) (in range)
  • Amboró National Park (180,000 ha) (in range)
  • Carrasco National Park (622,600 ha) (in range)
  • Noel Kempff Mercado National Park (1,500,000 ha) (Wallace et al. 1998)
  • Isiboro-Secure National Park (1,200,000 ha) (in range)
  • Ríos Blanco y Negro National Reserve (1,423,900 ha) (Wallace et al. 2000)
  • Beni Biosphere Reserve / Beni Biological Station (135.274 ha) (Garcia and Tarifa 1988, Painter et al. 1995)

Brazil

  • Amazônia National Park (1,114,917 ha) (in range)
  • Serra do Divisor National Park (846,408 ha) (in range)
  • Serra da Cutia National Park (284,923 ha) (in range)
  • Pacaás Novos National Park (708,664 ha) (in range)
  • Mapinguari National Park (1,572,422 ha) (in range)
  • Abufari Biological Reserve (224,819 ha) (in range)
  • Jaru Biological Reserve (353,386 ha) (in range)
  • Guaporé Biological Reserve (618,173 ha) (in range)
  • Jutaí-Solimões Ecological Station (287,101 ha) (in range)
  • Rio Acre Ecological Station (79,418 ha) (in range)
  • Iquê Ecological Station (217,184 ha) (in range)
  • Cuniã Ecological Station (49,886 ha) (in range)

Peru

  • Manu National Park (Soini et al. 1989)
  • Bahuaja-Sonene National Park (1,091,416 ha) (in range)
  • Pacaya-Samiria National Reserve (2,080,000 ha) (Aquino and Encarnación 1994)


It is included on Appendix II of CITES.


Questions? Comments? Suggestions? Additions?
Please contact The Virtual Zoo Staff


You are visitor count here since 21 May 2013

page design & content copyright © 2025 Andrew S. Harris

return to virtualzoo.org home

This page reprinted from http://www.virtualzoo.org. Copyright © 2025 Andrew S. Harris.

The Virtual Zoo, San Jose, CA 95125, USA