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TAXONOMY
Suborder: Haplorrhini
Infraorder: Simiiformes
Superfamily: Cercopithecidae
Family: Cercopithecidae
Genus: Papio
Species: P.cynocephalus
Subspecies: P. c. cynocephalus, P.c. ibeanus, P. c. kindae
Other names: P. cynocephalus: Papio hamadryas cynocephalus; cynocephalus baboon or savanna baboon; baviaan (Dutch); babouin jaune (French); babbuino (Italian); babian, babuin, or gul babian (Swedish); P. c. ibeanus: Ibean baboon; P. c. kindae: Kinda baboon
Total population: Unknown
Regions: Angola, Democratic Republic of Congo, Ethiopia, Kenya, Malawi, Mozambique, Somalia, Tanzania, Zambia
Gestation: 180 days (6 months)
Height: 1200 mm (M), 976 mm (F)
Weight: 25.8 kg (M), 11.0 kg (F)
The scientific name for yellow baboons comes from the Greek words kynos and kephalikos, meaning dog and head, respectively. This moniker refers to the quadrupedal stance seen in all baboons as well as the elongated muzzle which makes baboons look like dogs compared to most other monkeys and apes, including humans, which have flat faces (Altmann & Altmann 1970). While Groves (2001) recognizes P. cynocephalus to be a separate species from other baboons, some taxonomists have suggested that all yellow baboons be classified as a subspecies of P. hamadryas (Jolly 1993).
MORPHOLOGY
Yellow baboons are aptly named for the yellow-brown fur which covers their bodies except for their undersides, including the inner surfaces of the limbs, cheeks, and patches of fur on either side of the muzzle, which are white (Rowe 1996; Groves 2001). Adult males and females have longer hair along their flanks compared to the rest of their bodies while males have longer fur at the nape of their necks (Groves 2001). Yellow baboons have a prominent brow ridge covered in yellow-gray fur, but the rest of their face appears black and is only finely covered with fur. Their ischial callosities are also black. They have a protruding muzzle, similar to a dog’s. Yellow baboons walk quadrupedally, with their tails held up slightly and curved away from the body. There is variation between subspecies in the tail position and shape (Groves 2001). All baboons are sexually dimorphic. Wild yellow baboon males have an average height of 1200 mm (3.94 ft) and weigh 25.8 kg (56.9 lb) while females measure 976 mm (3.20 ft) and weigh only 11.0 kg (24.3 lb), on average (Altmann et al. 1993). Variation in length and sharpness of canine teeth is also seen among males and females. Male baboons have long, sharp upper canine teeth compared to females. They use their canines in aggressive interactions with other males and when feeding on large vertebrate prey (Walker 1984; Altmann pers. comm.).
Subspecific differences are slight among yellow baboons. Papio cynocephalus cynocephalus infants are born with a black natal coat that changes to the adult coloration as they age, while P. c. kindae infants have red coats at birth and P. c. ibeanus are born white (Groves 2001; Jolly & Phillips-Conroy 2005). Young baboons lose their natal coat starting at six months of age and have adult coloration by the end of month nine (Altmann pers. comm.). Other differences between subspecies include tail shape, body size, and pelage color. “Broken tails” are seen in P. c. cynocephalus; the tail is held almost horizontally away from the body and then falls abruptly, appearing broken. The other species have more gently curved tails. Differences in body size between subspecies can be seen in P. c. kindae , which is much smaller than other subspecies. Papio cynocephalus kindae males are about the same size as females of the other two subspecies and the females are proportionately smaller than the males (Jolly 1993). Finally, unlike the other subspecies, P. c. ibeanus has wavy instead of straight body hair (Groves 2001).
Like other cercopithecines, yellow baboons have cheek pouches, sacs in the lower portion of the cheek wall that can be used to store food. Moving between the cheek pouch and the oral cavity through a slit-like opening, food can be stored in the cheek pouch for consumption at a later time (Lambert & Whitham 2001).
Longevity in wild female yellow baboons is estimated to be around 14 to 15 years, but females have been recorded living up to 27 years in the wild (Rhine et al. 2000). Because of their social system and patterns of dispersal, it is more difficult to estimate male longevity in the wild (Altmann et al. 1988). The maximum lifespan in captivity is 40 years (Ross 1991).
RANGE
CURRENT RANGE MAPS (IUCN REDLIST):
Papio cynocephalus
Yellow baboons are found in central Africa from the west to eastern coasts in Angola, Zambia, Malawi, Mozambique, Tanzania, Kenya, and Somalia (Groves 2001). From east of the Luangwa River in Zambia, into Malawi, northern Mozambique, and most of Tanzania, P. c. cynocephalus can be found. Papio cynocephalus ibeanus is found in Kenya and southern Somalia and may range into southeastern Ethiopia while P. c. kindae is found in eastern Angola, southwestern Zambia, and parts of southern Democratic Republic of Congo (Jolly 1993; Groves 2001). There are some areas of overlap in the range of P. cynocephalus and other baboon (Papio) species, but levels of hybridization differ. For example, in Zambia and Angola, P. c. kindae overlaps with P. ursinus subspecies but there is not evidence of interbreeding (Jolly 1993). On the other hand, in Kenya, P. c. ibeanus overlaps with P. anubis and forms a hybrid zone, an area in which individuals show unusual phenotypic diversity resulting from ongoing crossbreeding between species (Samuels & Altmann 1986; Alberts & Altmann 2001). The crossbreeding of P. cynocephalus and P. anubis in this area may have contributed to the formation of the subspecies P. c. ibeanus (Alberts & Altmann 2001).
Long-term research on yellow baboons has been conducted since 1971 by Jeanne and Stuart Altmann, Susan Alberts, and their colleagues at Amboseli National Park, in southern Kenya on the border of Tanzania. At Mikumi National Park, Tanzania, Ramon Rhine and others have been studying yellow baboons since 1974. Yellow baboons have also been studied at Ruaha National Park, Tanzania and at the Tana River National Primate Reserve, Kenya. There are virtually no published studies of yellow baboons in Angola, Mozambique, or Malawi, countries that are plagued by civil war and where it is impossible for scientists to study baboon behavior.
HABITAT
Yellow baboons inhabit thorn scrub, savanna, open woodland, and gallery forests throughout their range (Rowe 1996). At Amboseli National Park, yellow baboons are found in semi-arid savannas with stands of acacia trees (Acacia xanthophloea and A. tortilis) breaking up the open grassland (Altmann & Altmann 1970). Because of the small amount of rainfall, they require proximity to water sources and are found in swamps and groundwater forests created from the underground drainage of Mount Kilimanjaro which rises above the park. Annual rainfall averages 335 mm (1.10 ft) and falls in two distinct periods, from November through December and March through May. In this marginal environment, the temperature ranges between 8.89 and 32.2° C (48 and 90° F) (Struhsaker 1967; Bronikowski & Altmann 1996). In the Tana River basin in eastern Kenya where yellow baboons are also found, mean monthly rainfall is much higher than at Amboseli, around 400 mm (1.31 ft) and the climate is slightly more temperate with average temperatures ranging between 22 and 34° C (71.6 and 93.2° F) (Wahungu 1998). The rainy seasons around the Tana River last from April to May and November to December, similar to the seasonal pattern at Amboseli (Wahungu 1998). Yellow baboons that are found in central Tanzania at Mikumi National Park live in the floodplain of the Mkata River (Norton et al. 1987). A mosaic of riverine forests and open grassland, which is seasonally flooded, are found in Mikumi and baboons do not range into the open grassland farther than 2 km (1.24 mi) from stands of trees. The warm, wet season lasts from November through May and the cold, dry season begins in June and continues through October. The average annual rainfall is 842 mm (2.76 ft) and temperatures range from 15 to 35° C (59 to 95° F) (Norton et al. 1987). Water is a limiting factor for baboon groups. The amount of rain determines the amount of standing water and therefore dictates the ranging patterns of baboon groups living in the park (Norton et al. 1987). In addition to being found in undeveloped savannas, yellow baboons are highly adaptable and can take to living alongside humans in rural areas developed for agriculture (Maples et al. 1976; Muoria et al. 2003).
ECOLOGY
Baboons have a diverse diet and are able to exploit a wide variety of foods, a necessity in an environment that is highly seasonal and in which the availability of food varies in abundance throughout the year. Yellow baboons have been called “eclectic omnivores,” because they are extremely selective in their foraging but they have a highly diverse diet (Altmann 1998). For example, in a study done at Mikumi National Park, Tanzania, yellow baboons were recorded eating plant parts from more than 180 species, but of those, only seven species were eaten throughout the year (Norton et al. 1987). Yellow baboons are highly dependent on reliable food sources including two species of acacia — the fever tree (Acacia xanthophloea) and the umbrella tree (A. tortilis) — grasses, and tubers (Altmann & Altmann 1970; Post 1982; Norton et al. 1987). In gallery forests and around permanent water holes, they consume all edible parts of the fever tree including leaves, gum, inner pith, blossoms, seeds, seed pods, and rotten wood. The umbrella tree, which grows in drier parts of their habitat, is utilized in a similar manner (Altmann & Altmann 1970). They also feed on grasses, stripping the seed heads from the blades and consuming the most nutritious part of the grass. During the dry season, they dig around the base of grass blades and consume the corms, which are fleshier and have more water content than the tips of the blades (Altmann & Altmann 1970). Immediately following the rainy season, when grass begins to sprout and is plentiful, they consume the entire blade (Wahungu 1998). Baboons are excellent diggers and utilize tubers, corms, and underground bulbs of plants throughout the year as well (Post 1982; Norton et al. 1987). In addition to grass, tubers, and acacia tree products, yellow baboons also feed on fruits, flowers, orthopterans, termites, beetles, ants, reptiles, birds, bird eggs, small vertebrate prey, and other primates including vervet monkeys (Chlorocebus aethiops) and lesser bush babies (Galago senegalensis). At the Tana River site where baboons are studied, fruit availability peaks after the rainy season and is at its lowest toward the end of the dry season. To cope with these seasonal changes in fruit availability, yellow baboons increase the frequency of consumption of invertebrates as well as eating more roots and tubers (Wahungu 1998).
Yellow baboons are reliant on essential localized resources such as water, food, and sleeping sites to determine their ranging patterns, therefore seasonal differences in daily range length and home range size are seen (Altmann 1974). At the Tana River study site, during the months following the end of the rainy season, baboons spend more time foraging and moving in gallery forests areas compared to the dry season, when they move into the open woodland and savanna (Wahungu 1998). The prevalence of fruit in the forest after the rainy season means they do not have to travel as far to obtain nutrient-rich foods and their daily path length is only about 3.4 km (2.11 mi) (Wahungu 2001). In the dry season, when fruits are scarce and foods in the forest are fewer compared to the savanna, yellow baboons expand their daily path movements to exploit as many food resources as are available, moving about 7.2 km (4.47 mi) each day (Wahungu 1998; 2001).
While most of the day is spent on the ground, baboons retreat to trees in nearby riverine or gallery forests overnight. Because of its size, the group is spread out over several trees, utilizing a sleeping grove rather than just a single tree (Wahungu 2001). Baboons center their home ranges around the main forested area where sleeping trees are located and return to the grove in the evenings (Wahungu 2001). The group leaves the sleeping grove between 7:00 and 10:00 a.m. each morning. After descending from the trees, the group either remains in the vicinity of the sleeping grove, socializing and grooming or moves into open grassland to forage (Altmann & Altmann 1970). Yellow baboons forage throughout the day, but there are peaks in social activity in the mid-morning, early to mid-afternoon and in the evening after entering the sleeping grove. As they forage, the group moves progressively further from the sleeping grove, but around mid-day, the group turns and begins to forage in the direction of the sleeping grove, working their way back to the forest and entering the sleeping grove between 5:30 and 6:45 p.m. (Altmann & Altmann 1970; Wahungu 2001).
One of the reasons baboons seek refuge in sleeping trees is to protect themselves from nocturnal predators. Potential predators include lions, cheetahs, leopards, spotted hyenas, jackals, pythons, chimpanzees (Pan troglodytes), felid-like predators such as servals, caracals, and genets, dogs, and humans (Altmann & Altmann 1970; Wahungu 2001).
SPECIAL NOTES
Baboons appear to be more closely related to humans and are therefore good candidates for animal models in biomedical research (Fridman & Popova 1988a). Yellow baboons, in particular, have been used in research on physiology, blood, the cardiovascular system, neurology, and endocrinology. They have also been used as an animal model to study organ transplantation, alcoholism, epilepsy, and high blood pressure (Fridman & Popova 1988b). About 6% of the biomedical studies involving nonhuman primates include baboon species (Carlsson et al. 2004). Changes in taxonomy and difficulty identifying species have made it impossible to evaluate which baboon species are used most frequently in research (Fridman & Popova 1988a).
Content last modified: January 6, 2006
Written by Kristina Cawthon Lang. Reviewed by Jeanne Altmann.
Cite this page as:
Cawthon Lang KA. 2006 January 6. Primate Factsheets: Yellow baboon (Papio cynocephalus) Taxonomy, Morphology, & Ecology . . Accessed 2020 July 2.
INTERNATIONAL STATUS
For individual primate species conservation status, please search the IUCN Red List.
Also search the current scientific literature for primate conservation status (overall as well as for individual species), and visit CITES (Convention on International Trade in Endangered Species of Wild Fauna and Flora).
Conservation information last updated in 2006 follows, for comparison:
CONSERVATION THREATS & POTENTIAL SOLUTIONS
Threat: Harvesting (hunting/gathering)
Hunting pressure on yellow baboons is increasing in some parts of their range and could reach unsustainable levels if it is not curtailed. Wildlife is the main source of protein for some people living in rural areas near forests, and when animals such as baboons, which are skilled crop-raiders, become nuisances, the harvesting increases to curb the population (FitzGibbon et al. 2000). The hunting pressure also increases as human population density increases. Eventually, hunting will extirpate those species that cannot reproduce quickly enough to replace members of the population lost to hunting (FitzGibbon et al. 2000). Yellow baboons, like other primates that have relatively slow reproductive rates, are likely to experience this population reduction as they cannot reproduce fast enough to compensate for the hunting in some areas. Though they are not threatened currently, decreasing local populations in and around forests decreases the overall conservation value of the forests and limits other activities such as ecotourism (FitzGibbon et al. 2000).
Threat: Accidental Mortality
While the yellow baboons are not threatened with extinction and are currently of little conservation concern, a pattern of accidental mortality has emerged among a group of baboons in Mikumi National Park, Tanzania. A highway connecting Tanzania and Zambia cuts through Mikumi, and baboons and other wildlife are increasingly threatened by fast-moving vehicles on this stretch of road. Constant improvements to road conditions allow drivers to increase their speed and subsequently more animal deaths have been reported (Drews 1995). About 18 yellow baboons are killed each year as a result of public traffic on the highway, and this cause of death can contribute up to 10% of the total yearly losses in each group. As roads are built and paved through remaining rural areas throughout the range of the yellow baboon, it is possible that collisions with vehicles can significantly decrease population growth in some areas (Drews 1995).
Threat: Changes in Native Species Dynamics
Natural changes in the ecosystem of Amboseli National Park resulted in high mortality among yellow baboons during the late 1960s. During this time, significant changes to the habitat occurred, though it is unclear if these changes directly affected the baboons or if they were indirectly responsible for the decrease in population size and density (Altmann 1998). The landscape at Amboseli was indirectly affected by human population growth in the areas surround the park. As the human population in surrounding areas grew, an attempt to separate the park from human areas through fencing caused the elephant population within the park to be confined. Some 700 elephants became restricted to the boundaries of the park and rather than moving over huge distances, foraging as they moved, the elephants remained inside the park, destroying fever trees ( Acacia xanthophloea ) and eliminating food sources and shelter for many mammals, including baboons (Cheney & Seyfarth 1990). Another source of mortality for the fever trees was the rising water table caused by runoff from Mount Kilimanjaro, which rises above Amboseli. These two factors played some role in the annual die-off of 46% of the population of yellow baboons in the park during the years from 1964-1969 (Altmann 1998).
LINKS TO MORE ABOUT CONSERVATION
ORGANIZATIONS INVOLVED IN Papio cynocephalus CONSERVATION
Chimfunshi Wildlife Orphanage
Gombe Stream Research Centre
Israeli Primate Sanctuary
Colobus Conservation
Content last modified: January 6, 2006
Written by Kristina Cawthon Lang. Reviewed by Jeanne Altmann.
Cite this page as:
Cawthon Lang KA. 2006 January 6. Primate Factsheets: Yellow baboon (Papio cynocephalus ) Conservation . . Accessed 2020 July 2.
REFERENCES
Alberts SC, Altmann J. 1995a. Balancing costs and opportunities: dispersal in male baboons. Am Natural 145(2): 279-306.
Alberts SC, Altmann J. 1995b. Preparation and activation: determinants of age at reproductive maturity in male baboons. Behav Ecol Sociobiol 36(6): 397-406.
Alberts SC, Altmann J. 2001. Immigration and hybridization patterns of yellow and anubis baboons in and around Amboseli, Kenya. Am J Primatol 53(4): 139-54.
Alberts SC, Altmann J, Wilson ML. 1996. Mate guarding constrains foraging activity of male baboons. Anim Behav 51(6): 1269-77.
Alberts SC, Watts HE, Altmann J. 2003. Queuing and queue-jumping: long-term patterns of reproductive skew in male savannah baboons, Papio cynocephalus. Anim Behav 65(4): 821-40.
Altmann J. 1980. Baboon mothers and infants. Chicago (IL): Univ Chicago Pr. 242 p.
Altmann SA, editor. 1967. The structure of primate social communication. In: Social communication among primates. Chicago (IL): Chicago Univ Pr. p 325-62.
Altmann SA. 1970. The pregnancy sign in savannah baboons. Lab Anim Med 6: 7-10.
Altmann SA. 1974. Baboon, space, time and energy. Am Zool 14: 221-48.
Altmann SA. 1998. Foraging for survival: yearling baboons in Africa. Chicago (IL): Univ Chicago Pr. 609 p.
Altmann J, Alberts SC. 2005. Growth rates in a wild primate population: ecological influences and maternal effects. Behav Ecol Sociobiol 57(5): 490-501.
Altmann SA, Altmann J. 1970. Baboon ecology: African field research. Chicago (IL): Univ Chicago Pr. 220 p.
Altmann J, Hausfater G, Altmann SA. 1988. Determinants of reproductive success in savannah baboons, Papio cynocephalus. In: Clutton-Brock TH, editor. Reproductive success: studies of individual variation in contrasting breeding systems. Chicago (IL): Univ Chicago Pr. p 403-18.
Altmann J, Schoeller D, Altmann SA, Muruthi P, Sapolsky RM. 1993. Body size and fatness of free-living baboons reflect food availability and activity levels. Am J Primatol 30(2): 149-61.
Bentley-Condit VK, Smith EO. 1999. Female dominance and female social relationships among yellow baboons (Papio hamadryas cynocephalus). Am J Primatol 47(4): 321-34.
Bronikowski AM, Altmann J. 1996. Foraging in a variable environment: weather patterns and the behavioral ecology of baboons. Behav Ecol Sociobiol 39(1): 11-25.
Buchan JC, Alberts SC, Silk JB, Altmann J. 2003. True paternal care in a multi-male primate society. Nature 425(6954): 179-81.
Carlsson HE, Schapiro SJ, Farah I, Hau J. 2004. Use of primates in research: a global overview. Am J Primatol 63(4): 225-37.
Cheney DL, Seyfarth RM. 1990. How monkeys see the world: inside the mind of another species. Chicago (IL): Univ Chicago Pr. 377 p.
Combes SL, Altmann J. 2001. Status change during adulthood: life-history by-product or kin selection based n reproductive value? Proc Royal Soc London 268: 1367-73.
Drews C. 1995. Road kills of animals by public traffic in Mikumi National Park, Tanzania, with notes on baboon mortality. Afr J Ecol 33(2): 89-100.
Drews C. 1996. Contexts and patterns of injuries in free-ranging male baboons (Papio cynocephalus). Behaviour 133(5-6): 443-74.
FitzGibbon CD, Mogaka H, Fanshawe JH. 2000. Threatened mammals, subsistence harvesting, and high human population densities: a recipe for disaster? In: Robinson JG, Bennett EL, editors. Hunting for sustainability in tropical forests. New York: Columbia Univ Pr. p 154-67.
Fridman EP, Popova VN. 1988b. Species of the genus Papio (Cercopithecidae) as subjects of biomedical research: I. Biological basis of experiments on baboons. J Med Primatol 17(6): 291-307.
Fridman EP, Popova VN. 1988a. Species of the genus Papio (Cercopithecidae, Primates) as subjects of biomedical research: II. Quantitative characteristics of contemporary use of baboon species in medical and biological investigations. J Med Primatol 17(6): 309-18.
Groves C. 2001. Primate taxonomy. Washington DC: Smithsonian Inst Pr. 350 p.
Hall KRL, DeVore I. 1965. Baboon social behavior. In: DeVore I, editor. Primate behavior: field studies of monkeys and apes. New York: Holt Rinehart Winston. p 53-110.
Hausfater G. 1975. Dominance and reproduction in baboons (Papio cynocephalus): a quantitative analysis. Contributions to primatology, Vol. 7. Basel (Switzerland ): S. Karger. 150 p.
Jolly CF. 1993. Species, subspecies, and baboon systematics. In: Kimbel WH, Martin LB, editors. Species, species concepts, and primate evolution. New York : Plenum Pr. p 67-107.
Jolly CF, Phillips-Conroy JE. 2005. “White babies” and the zone of contact and probably intergradation among three distinct baboon allotaxa in the Luangwa valley, Zambia [Abstract]. Am J Phys Anthro Suppl 40: 123.
Lambert JE, Whitham JC. 2001. Cheek pouch use in Papio cynocephalus. Folia Primatol 72(2): 89-91.
Maples WR, Maples MK, Greenhood WF, Walek ML. 1976. Adaptations of crop-raiding baboons in Kenya. Am J Phys Anthro 45: 309-16.
Muoria PK, Karere GM, Moinde NN, Suleman MA. 2003. Primate census and habitat evaluation in the Tana delta region, Kenya. Afr J Ecol 41(2): 157-63.
Noë R, Sluijter AA. 1995. Which adult male savanna baboons form coalitions? Int J Primatol 16(1): 77-105.
Norton GW, Rhine RJ, Wynn GW, Wynn RD. 1987. Baboon diet: a five-year study of stability and variability in the plant feeding and habitat of the yellow baboons (Papio cynocephalus) of Mikumi National Park, Tanzania . Folia Primatol 48(1-2): 78-120.
Post DG. 1982. Feeding behavior of yellow baboons (Papio cynocephalus) in the Amboseli National Park, Kenya. Int J Primatol 3(4): 403-30.
Rasmussen KLR. 1986. Spatial patterns and peripheralisation of yellow baboons (Papio cynocephalus) during sexual consortships. Behaviour 97(1-2): 161-80.
Rhine RJ, Norton GW, Wasser SK. 2000. Lifetime reproductive success, longevity, and reproductive life history of female yellow baboons (Papio cynocephalus) of Mikumi National Park, Tanzania. Am J Primatol 51(4): 229-41.
Rhine RJ, Norton GW, Wynn GM, Wynn RD. 1985. Weaning of free-ranging infant baboons (Papio cynocephalus) as indicated by one-zero and instantaneous sampling of feeding. Int J Primatol 6(5): 491-9.
Ross C. 1991. Life history patterns of New World monkeys. Int J Primatol 12(5): 481-502.
Rowe N. 1996. The pictorial guide to the living primates. East Hampton (NY): Pogonias Pr. 263 p.
Samuels A, Altmann J. 1986. Immigration of a Papio anubis male into a group of Papio cynocephalus baboons and evidence for an anubis- cynocephalus hybrid zone in Amboseli, Kenya. Int J Primatol 7(2): 131-8.
Samuels A, Altmann J. 1991. Baboons of the Amboseli Basin: demographic stability and change. Int J Primatol 12(1): 1-19.
Samuels A, Silk JB, Altmann J. 1987. Continuity and change in dominance relations among female baboons. Anim Behav 35(3): 785-93.
Semple S, McComb K, Alberts S, Altmann J. 2002. Information content of female copulation calls in yellow baboons. Am J Primatol 56(1): 43-56.
Silk JB, Alberts SC, Altmann J. 2004. Patterns of coalition formation by adult female baboons in Amboseli, Kenya. Anim Behav 67(3): 573-82.
Stein DM. 1984. Ontogeny of infant-adult male relationships during the first year of life for yellow baboons (Papio cynocephalus). In: Taub DM, editor. Primate paternalism. New York: Van Nostrand Reinhold. p 213-43.
Struhsaker TT. 1967. Ecology of vervet monkeys (Cercopithecus aethiops) in the Masai-Amboseli Game Reserve, Kenya. Ecology 48: 891-904.
Wahungu GM. 1998. Diet and habitat overlap in two sympatric primate species, the Tana crested mangabey Cercocebus galeritus and yellow baboon Papio cynocephalus. Afr J Ecol 36(2): 159-73.
Wahungu GM. 2001. Common use of sleeping sites by two primate species in Tana River, Kenya. Afr J Ecol 39(1): 18-23.
Walker A. 1984. Mechanisms of honing in the male baboon canine. Am J Phys Anthro 65(1): 47-60.
Content last modified: January 6, 2006
IMAGES
Papio cynocephalus Photo: Dennis Rasmussen |
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Papio cynocephalus Photo: Dennis Rasmussen |
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Papio cynocephalus Photo: Irwin S. Bernstein |
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Papio cynocephalus Photo: J. Stephen Gartlan |
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Papio cynocephalus Photo: Kathryn L. Rasmussen |
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Papio cynocephalus Photo: Kathryn L. Rasmussen |
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Papio cynocephalus Photo: Kathryn L. Rasmussen |
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Papio cynocephalus Photo: Kathryn L. Rasmussen |
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Papio cynocephalus Photo: Kathryn L. Rasmussen |
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Papio cynocephalus Photo: Kathryn L. Rasmussen |
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Papio cynocephalus Photo: Kathryn L. Rasmussen |
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Papio cynocephalus Photo: Kathryn L. Rasmussen |
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Papio cynocephalus Photo: Kathryn L. Rasmussen |
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Papio cynocephalus Photo: Mark Murchison |
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Papio cynocephalus Photo: Mark Murchison |
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Papio cynocephalus Photo: S. J. Bleiwess |
Cite this page as: Cawthon Lang KA. 2006 January 6. Primate Factsheets: Yellow baboon ( Papio cynocephalus ) Taxonomy, Morphology, & Ecology . . Accessed 2020 July 2.
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