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TAXONOMY
Suborder: Haplorrhini
Infraorder: Simiiformes
Superfamily: Hominoidea
Family: Hominidae
Genus: Pan
Species: P. paniscus
Other names: bonobo chimpanzee, gracile ape, lesser chimpanzee, or pygmy chimpanzee; chimpanzeé nain or chimpanzeé pygmée (French); chimpancé pigmeo (Spanish); bonobo or dvärgschimpans (Swedish)
The name bonobo is meaningless; it is probably derived from a misspelling on a shipping crate going to Bolobo, Zaire (now Democratic Republic of Congo) (de Waal 1997).
MORPHOLOGY
Bonobos are sometimes called pygmy chimpanzees even though they are about the same size as chimpanzees (Pan troglodytes). Overall, they have a more gracile, or slender, build than chimpanzees. They exhibit moderate sexual dimorphism with adult males weighing about 39 kg (86.0 lb) and, on average, measuring 730 to 830 mm (2.40 to 2.72 ft) tall while adult females weigh about 31 kg (68.3 lb) and are about 700 to 760 mm (2.3 to 2.49 ft) tall (Rowe 1996).
Bonobos have black hair and black faces from birth. The hair on their head looks as if it is parted and they do not tend to go bald with age as is seen in chimpanzees. Bonobos are also born with a white rump tuft (Rowe 1996; de Waal 1997).
Locomotion patterns in bonobos include quadrupedal knuckle walking, modified brachiation and some bipedalism (Rowe 1996). Bonobos show a greater predisposition for bipedal gait than other apes because of a more centrally positioned foramen magnum, longer thigh bones, longer feet, and differential distribution of body weight (Myers Thompson 2002).
The average lifespan of bonobos is 40 years (Rowe 1996).
RANGE
Bonobos are confined to a 200,000 km² (77,220 mi²) area in central Africa in the Democratic Republic of Congo (DRC). This area, roughly the size of Great Britain, in the central basin of the DRC, contains two river systems that converge to define the extent of bonobo distribution: the Congo-Zaire-Walaba River and the Kwa-Kasai-Sankuru River (Kortlandt 1995). These rivers serve as an effective geographical barrier for the apes as they are not known to swim (though they have been seen wading into waist-deep water) (Kortlandt 1995; Myers Thompson 2002). IUCN Redlist estimates a minimum range size of 500,000 km² (IUCN Redlist).
Estimates of wild populations are few and varied, with numbers as low as 5,400 up to 100,000 individuals (Kortlandt 1995; Thompson-Handler et al. 1995). These numbers may be considered overly optimistic, though, and the true population size is unknown (Coxe et al. 2000). IUCN Redlist reports a population estimate of at least 29,500 individuals (IUCN Redlist). There are about 150 individuals in captivity (ISIS.org).
Most fieldwork has been conducted in two sites, Lomako and Wamba, but other research sites include Lilungu (Ikela), Yalosidi, Yasa, and Tumba. The bonobos at the Wamba study site have been observed since 1974 and are provisioned with food such as sugarcane (de Waal 1997).
HABITAT
Bonobos exploit the swampy rainforest south of the Zaire River. They forage in swamp meadows on a thin underlying peat layer. The semideciduous trees that this area supports produce fleshy fruits adapted to mammal dispersion. These trees are part of a secondary forest ecosystem and are generally in intermediate and older stages of development. These forests are also known as subclimax forests (Kortlandt 1995). At one of the field sites, Lukuru, there is an absence of swamp vegetation and bonobos utilize the mosaic of dry forest and savanna habitats (Myers Thompson 2002).
The average monthly air temperature in this region is between 20° to 30° C (68° to 86° F). The annual rainfall in this area is between 1600 and 2000 mm (5.25 and 6.56 ft) (Kano 1992).
ECOLOGY
The population density of bonobos is hard to estimate, but some studies have put it at 0.4 individuals per km² (.249 per mi²) (Kano 1992; Kortlandt 1995). Even in the most densely populated areas, these apes have a patchy distribution.
Their diet consists mainly of plant products including fruit, seeds, sprouts, leaves, flowers, bark, stems, pith, roots, and mushrooms. Though the majority of their diet is fruit (57%), bonobos are also known to consume small mammals, insect larvae, earthworms, honey, eggs, and soil (Kano 1992; Bermejo et al. 1994). Unlike chimpanzees, bonobos do not actively hunt mammalian prey but feed on it opportunistically (White 1996). At one study site, bonobos have been observed washing off their food before eating (Bermejo et al. 1994).
Daily activities can be partitioned into six categories: feeding in trees, rest, travel, foraging, nest-building, and group excitement. These daily activities are generally in a cycle of resting (43% of the day), traveling (13%), foraging (20%), and feeding (20%). The remaining time is spent doing other activities. Bonobos forage for principal food items between 25 and 40 m (82 and 131 ft) above the ground. Though most primary food sources are found at this height, they will not ingest food found at this height if there is not a secure substrate (Kano 1992). Their average daily travel distance is 2.0 km (1.24 mi) (Kano 1992). Because of the relative richness of their habitat and availability of food sources, there is little constraint on bonobo group size. The result is a decrease in intraspecific feeding competition and heightened sociality, especially between females (Blount 1990).
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 2010 follows, for comparison:
CONSERVATION THREATS & POTENTIAL SOLUTIONS
Threat: Human Induced Habitat Loss and Degradation
Habitat loss and degradation due to commercial logging, subsistence usage of forest products, and re-emigration into the forest by local human populations is prevalent in DRC and greatly threatens bonobo populations (Dupain et al. 2000). Large-scale commercial logging is responsible for more damage than simply removal of forest cover; some of its byproducts include loss of biodiversity, climate change, desertification, and watershed degradation (Rowe et al. 1992). These indirect environmental consequences are of serious concern for bonobo populations, even at well-established research sites that exist on logging concessions (Oates 1995; Thompson-Handler 1995). There is continuing concern that the Congolese government will begin to rely more heavily on timber extraction as its key economic opportunity and depend on forest resources for fiscal development. Because of these future plans, commercial logging is the perceived to be the largest threat to bonobos in DRC over the long-term (Reinartz & Bila Isia 2001).
More ubiquitous as a cause of habitat loss and degradation is the conversion of forest to agricultural lands as well as collection of firewood for subsistence usage and for sale in urban centers (Thompson-Handler et al. 1995). Profits from agricultural products traditionally harvested in semi-rural areas and sold in markets in urban centers have plummeted due to the deterioration of the economy, roads, and the river transport system associated with the political instability (Dupain et al. 2000). While this may temporarily mitigate habitat destruction due to agriculture, the resulting trend is re-immigration of local people into the forests and subsequent establishment of semi-permanent settlements. In these establishments, people practice small-scale cultivation and subsistence hunting as well as collection of wood for fuel and shelter (Dupain et al. 2000; Reinartz & Bila Isia 2001). While some areas have protected status, this is merely a label that has no meaning; a total lack of laws and enforcement creates a climate in which people can live within the boundaries of the park and use the natural resources without consequences (Coxe et al. 2000).
Potential Solutions
Logging threats may be temporarily mitigated, though, because of the political instability and warfare that have plagued DRC for almost a decade. Logging companies have ceased their activities because of the dangers of working in a combat zone and as a result, habitat loss due to the extraction of trees and the infrastructure associated with unsustainable forestry techniques has ceased (Dupain et al. 2000). It is important, though, that when lands slated for logging become available in the future, that bonobo-friendly forestry techniques are used. That is, low impact, sustainable logging should be the goal of the Congolese government, especially if timber is to be the most important export commodity and the basis of its economic viability.
With only two reserves (Salonga National Park and Luo River Scientific Reserve) where bonobos occur and logging is prohibited, an important goal for the future is to create more protected areas as well as increase protection of bonobos both in and outside existing reserves (Reinartz & Bila Isia 2001).
Unfortunately, little can be done to alleviate the impacts of habitat loss due to subsistence agriculture and fuelwood collection at this time. Many Congolese have been displaced and have no other economic or even subsistence opportunities, and until there is stability in DRC, most research has ceased and bonobo populations cannot be reliably protected (Coxe et al. 2000).
Threat: Invasive Alien Species
There are a number of pathogenic and parasitic diseases that affect bonobos in the wild. Respiratory, gastrointestinal, cutaneous, or systemic bacterial infections can range in severity from latency to death (Whittier et al. 2001). Salmonella, Steptococcus, and Staphylococcus are common agents that can be found within the environment or can be transferred between humans and bonobos (Whittier et al. 2001). Other infectious agents that affect bonobos include viruses (poliovirus, measles, herpes, hepatitis, Ebola, etc.), fungal infections (ringworm), and parasites, both ectoparasitic and endoparasitic (Giardia, Cryptosporidium, Schistosoma, Strongyloides, etc.) (Whittier et al. 2001). While there may be some natural background rate of these diseases, certainly epidemics of some could threaten entire populations of bonobos. Unnatural exposure to these and other diseases could lead to rapid extinction in non-immune bonobos or very small populations of bonobos. As humans and bonobos come into close contact because of population growth, habituation to researchers, and hunting, the probability of disease transmission between species increases (Butynski 2001).
Potential Solutions
At research sites, precautions should be taken to ensure minimal exposure. This includes screening researchers and visitors, updating vaccinations (where applicable), limiting contact, and burying human waste (Whittier et al. 2001). Health education about zoonotic diseases in local communities may also decrease the incidence of disease transfer between bonobos and humans.
Threat: Harvesting (hunting/gathering)
As the population explodes in Central Africa, traditional values are eroded as are time-honored tribal customs. This is important in the case of the bonobo because across many tribes in DRC, it has been traditionally taboo to hunt these apes, though that sentiment is quickly falling by the wayside (Thompson-Handler et al. 1995; Coxe et al. 2000). With no other economic opportunities, local people must trade bushmeat for clothes, medicines, soap, spices, and other necessities as well as use it as a primary protein source (Dupain & Van Elsacker 2001). Moreover, with an active zone of military occupation bisecting the bonobo’s range, troops and displaced people consume bushmeat as a main source of protein and rely on its sale as a source of income (Reinartz & Bila Isia 2001).
The role of lumber companies in the bushmeat market cannot be underestimated. They provide guns and ammunition, transportation to and from the forests where bonobos are hunted, boats to move carcasses between the forest and urban centers, and workers hunt, sell, and eat the meat (Butynski 2001; Dupain & Elsacker 2001). Guns have also become quite prolific and readily available as the civil war erupted (Coxe et al. 2000).
Infant bonobos are also highly prized as pets, and as adult bonobos are killed for meat, infants are sold in markets in urban centers such as Kinshasa. It is estimated that between five and 10 adults are killed to capture one infant, as reproductive-aged adults are culled from the population, the reproductive capacity of the population will dwindle (Reinartz & Bila Isia 2001).
Potential Solutions
Foreign logging companies must be held accountable for their roles in the bushmeat trade. Instead of facilitating the illegal hunting, transportation, sale, and consumption of bonobos, logging companies should provide alternate food sources for their employees and prohibit the transportation of meat and hunting paraphenelia on company boats (Dupain & Van Elsacker 2001).
Local communities that depend on bonobo meat for protein and as currency to obtain necessary supplies should be provisioned with alternate food sources and sundries by international aid organizations. Giving people alternatives may alleviate some of the pressure on bonobo populations in the most heavily hunted areas. Providing other economic opportunities is another crucial factor in decreasing reliance on bushmeat. In times of peace, this can be achieved by maintaining a strong research presence in areas that have been traditionally used as hunting grounds (Dupain & Van Elsacker 2001). Researchers can often provide jobs to local people as field assistants, educators, and camp staff. They not only offer paid work, but having locals involved in research and bonobo conservation creates a meaningful connection between people and wildlife that may influence their future actions (Wrangham 2001).
Educating potential buyers of infant bonobos in the markets of Congolese urban centers is another way to decrease the market for apes as pets.
Threat: Accidental Mortality
Occasionally bonobos are ensnared in traps set for other terrestrial mammals and are injured (Kano 1992; Coxe et al. 2000). There is little data on the scope of this problem.
Threat: Persecution
Traditionally, bonobos were revered and viewed as relatives to local people (Coxe et al. 2000). Where they are not habituated, bonobos are extremely shy and afraid of people (de Waal 1996). Except for where they are hunted as food, there are no instances of human-bonobo conflict.
Threat: Changes in Native Species Dynamics
Bonobos have no known predators and as such their population size and structure is not affected by predator-prey interactions (de Waal 1996).
At Wamba, there have been high instances of physical handicaps noted in the study groups. Missing digits and limbs dominate those deformities recorded, and there is some speculation that leprosy could be one of the causes of these abnormalities (Kano 1992).
Potential Solutions
Limiting physical contact between bonobos and humans is crucial to minimizing transfer of all diseases. In instances where it is appropriate and the bonobos are habituated, veterinary care may also be helpful.
Threat: Intrinsic Factors
Bonobos are long-lived and mature slowly, producing few offspring over their lifetimes, as such population growth rates are inherently slow. Because of these qualities, disturbances can have significant affects on overall population size (Thompson-Handler et al. 1995). Any demographic changes are compounded by the effects of habitat fragmentation, range restriction, and decreasing population sizes. For example, when two populations that used to come into contact are separated by an impassable barrier, such as a logging road, gene flow between the two communities ceases and problems such as inbreeding depression and subsequent fixation of deleterious alleles (Thompson-Handler et al. 1995; Coxe et al. 2000).
Potential Solutions
Efforts to decrease habitat fragmentation should be of greatest importance. Demographic changes should be minimized, if at all possible, by decreasing the demand for bushmeat as well as setting up orphanages and refuges for infant bonobos confiscated in markets.
Captive breeding programs are also important and may serve as “arks” for bonobos. It should continue to be the goal of programs to produce and maintain viable populations ex situ.
Threat: Human Disturbance
Political instability has had deleterious effects on all life in DRC and continues to impede bonobo conservation and research efforts. All research has been abandoned in this area, and few reports of bonobo populations at the most important study sites are available. In some cases, those local people involved in the research have managed to stay and serve as guards, though they are unable to receive any salaries from researchers and communication is impossible. Where bonobos have been habituated, their risk of being shot by soldiers and hunters is great, and research assistants have little means to protect these apes from such persecution (Coxe et al. 2000).
Potential Solutions
There are few options as long as the area remains insecure for both foreign and domestic assistance and involvement (Coxe et al. 2000).
LINKS TO MORE ABOUT CONSERVATION
CONSERVATION INFORMATION
- African Great Apes (WWF African Great Apes Programme, January 2005)
- Best Practice Guidelines for the Re-introduction of Great Apes (IUCN/SSC Primate Specialist Group)
- Slaughter of the Apes (October 13, 2006)
- The Bonobo Conservation Inititative
- Links for all species
CONSERVATION NEWS
- Why are We Eating Bonobos? Can We Save Africa’s Vast Wildernesses from Destruction? (National Geographic; October 14, 2012)
- Conservationist devotes life to bonobos (Marion Star; December 5, 2010)
- Going Ape in Central Africa: Meeting Our Closest Cousins in the Near-Wild Within Easy Reach of Major Cities (Huffington Post; October 12, 2010)
- Into the Congo: saving bonobos means aiding left-behind communities, an interview with Gay Reinartz (Mongabay; September 23, 2010)
- Bonobos going wild (Charlotte Observer; July 6, 2009)
- Reintroducing Bonobo Apes Into The Wild: Researchers To Monitor Progress (ScienceDaily; June 15, 2009)
- New rainforest reserve in Congo benefits bonobos and locals (Mongabay; May 25, 2009)
- Massive New Rainforest Reserve Established in the Democratic Republic of Congo (Yubanet; November 16, 2007)
- Best Practice Guidelines for the Re-introduction of Great Apes (IUCN/SSC Primate Specialist Group)
- ‘Protected’ Congo forest is logged regardless (New Scientist; April 11, 2007)
- Illegal Loggers Mutilating Congolese Forests (Environment News Service; February 28, 2007)
- Trust’s donations save apes worldwide (Des Moines Register; December 15, 2006)
- Monkey business (Carte Blanche; October 29, 2006)
- Great Ape Trust Awards $22,000 in Conservation Grants (E-Wire; August 22, 2006)
- Bush-meat traders threaten Nigeria’s chimps (Georgia Straight, Canada; November 3, 2005)
- Woods Hole Research Center scientist part of international initiatives to save the great apes (EurekAlert; October 11, 2005)
- New Conservation Groups Formed at World Wilderness Congress (Environment News Service; October 10, 2005)
- Conservationists seek to protect apes (Associated Press; July 27, 2005)
- Expert highlights mobile phone threat to great apes (Australian Broadcasting Company; March 10, 2005)
- Study links Ebola outbreaks to animal carcasses (EurekAlert; February 14, 2005)
- Pygmy chimpanzees on the brink of extinction (Independent Online, South Africa; January 10, 2005)
- Fences ‘can help apes’ survival’ (BBC News; May 5, 2004)
- African apes being eaten into extinction (Sunday Herald, UK; October 11, 2003)
- African `bushmeat’ trade raises health, conservation fears (Taipei Times; August 25, 2003)
- Balancing Wildlife Conservation with Human Survival (Inter Press Service News Agency; October 11, 2003)
- Bonobos’ threat: hungry humans (Christian Science Monitor; June 7, 2001)
- Dire Outlook for Many Primates (BBC; May 12, 2000)
- Eating apes imperils species, spreads AIDS (ABC Science Online, Australia; September 15, 2003)
- Great apes in peril (BBC News; May 20, 2001)
- Growing demand for ‘bushmeat’ threatens great apes (CNN; August 11, 1999)
- Last chance to save great apes from extinction (Guardian Unlimited; May 21, 2001)
- Links for all species
ORGANIZATIONS INVOLVED IN Pan paniscus CONSERVATION
- Bonobo Conservation Initiative
- Jane Goodall Institute France
- Paniscus
- Projet Protection des Gorilles
Content last modified: December 1, 2010
Written by Kristina Cawthon Lang. Reviewed by Frans de Waal.
Cite this page as:
Cawthon Lang KA. 2010 December 1. Primate Factsheets: Bonobo (Pan paniscus) Conservation . <http://pin.primate.wisc.edu/factsheets/entry/bonobo/cons>. Accessed 2020 July 29.
REFERENCES
Badrian A & Badrian N. 1984. Social organization of Pan paniscus in the Lomako forest, Zaire. In: Susman RL, editor. The pygmy chimpanzee: evolutionary biology and behavior. New York: Plenum Pr; p. 325-46.
Bermejo J, Illera G, Sabater Pi JS. 1994. Animals and mushrooms consumed by bonobos (Pan paniscus). Int J Prim 15(6): 879-98.
Blount BG. 1990. Issues in bonobo (Pan paniscus) sexual behavior. Am Anthro 92(3): 702-14.
Coxe S, Rosen N, Miller P, Seal U, editors. Bonobo conservation assessment workship final report; 1999 Nov 21-22; Inuyama, Japan. Apple Valley (MN): IUCN/SSC Conservation Breeding Specialist Group. 51 p.
Dupain J, van Elsacker L. 2001. Status of the proposed Lomako Forest Bonobo Reserve: a case study of the bushmeat trade. In: Galdikas BMF, Erickson Briggs N, Sheeran LK, Shapiro GL, Goodall J, editors. All apes great and small. Volume 1, African apes. New York: Kluwer Academic/Plenum. p 259-273.
Dupain J, Van Elsacker L, Nell C, Garcia P, Ponce F, Huffman MA. 2002. New evidence for leaf swallowing and Oesophagostomom infection in bonobos (Pan paniscus). Int J Prim 23(5): 1053-62.
Dupain J, Van Krunkelsven E, Van Elsacker L, Verheyen, RF. 2000. Current status of the bonobo (Pan paniscus) in the proposed Lomako Reserve (Democratic Republic of Congo). Bio Cons 94(2000): 265-72.
Furuichi T. 1989. Social interactions and the life history of female Pan paniscus in Wamba, Zaire. Int J Prim 10(3): 855-75.
Furuichi T, Idani G, Ihobe H, Kuroda S, Kitamura K, Mori A, Enomoto T, Okayasu N, Hashimoto C, Kano T. 1998. Population dynamics of wild bonobos (Pan paniscus) at Wamba. Int J Prim 19(6): 1029-43.
Groves C. 2001. Primate taxonomy. Washington DC: Smithsonian Inst Pr. 350 p.
Hohmann G, Gerloff U, Tautz D, Fruth B. 1999. Social bonds and genetic ties: kinship, association, and affiliation in a community of bonobos (Pan paniscus). Behaviour 136: 1219-35.
Kano T. 1992. The last ape: pygmy chimpanzee behavior and ecology. Stanford (CA): Stanford Univ Pr. 248 p.
Kano T. 1996. Male rank order and copulation rate in a unit-group of bonobos at Wamba, Zaire. In: McGrew WC, Marchant LF, Nishida T, editors. Great ape societies. Cambridge (England): Cambridge Univ Pr; p 135-45.
Kortlandt A. 1995. A survey of the geographical range, habitats and conservation of the pygmy chimpanzee (Pan paniscus): an ecological perspective. Prim Cons 16: 21-36.
Kuroda S. 1989. Developmental retardation and behavioral characteristics of pygmy chimpanzees. In: Heltne PG, Marquardt LA, editors. Understanding chimpanzees. Cambridge (MS): Harvard Univ Pr; p 184-93.
Malenky RK, Thompson-Handler N, Susman RL. 1989. Conservation status of Pan paniscus. In: Heltne PG, Marquardt LA, editors. Understanding chimpanzees. Cambridge (MS): Harvard Univ Pr; p 362-70.
Oates JF, compiler. 1995. Status survey and conservation action plan: African primates (Revised edition). Gland (Switzerland): IUCN/SSC Primate Specialist Group. 80 p.
Reichert KE, Heistermann J, Hodges K, Boesch C, Hohmann G. 2002. What females tell males about their reproductive status: are morphological and behavioral cues reliable signals of ovulation in bonobos (Pan paniscus)?. Ethology 108: 583-600.
Reinartz G & Bila Isia I. 2001. Bonobo survival and a wartime conservation mandate. In: The apes: challenges for the 21st century. Conference proceedings; 2000 May 10-13; Brookfield, IL. Chicago: Chicago Zoo Soc; p 52-6.
Rowe N. 1996. The pictorial guide to the living primates. East Hampton (NY): Pogonias Pr. 263 p.
Rowe R, Sharma N, Browder J. 1992. Deforestation: problems, causes and concerns. In: Sharma NP, editor. Managing the world’s forests: looking for balance between conservation and development. Dubuqe (IA): Kendall/Hunt. P 33-45.
Savage-Rumbaugh S, Lewin R. 1994. Kanzi: the ape at the brink of the human mind. New York: J Wiley. 299 p.
Thompson-Handler N, Malenky RK, Badrian N. 1984. Sexual behavior of Pan paniscus under natural conditions in the Lomake forest, equateur, Zaire. In: Susman RL, editor. The pygmy chimpanzee: evolutionary biology and behavior. New York: Plenum Pr; p 347-68.
Thompson-Handler N, Malenky RK, Reinartz GE, editors. 1995. Action plan for Pan paniscus: report of free-ranging populations and proposals for their preservation. Milwaukee (WI): Zoo Soc Milwaukee County. 105 p.
Vervaecke H, Van Elsacker L, Mohle M, Heistermann M, Verheyen RF. 1999. Inter-menstrual intervals in captive bonobos (Pan paniscus). Primates 40(2): 283-9.
de Waal, FB. 1988. The communicative repertoire of captive bonobos (Pan paniscus) compared to that of chimpanzees. Behaviour 106: 183-251.
de Waal FB. 1997. Bonobo: the forgotten ape. Berkelely (CA): Univ California Pr. 210 p.
de Waal FB. 2001. The ape and the sushi master: cultural reflections by a primtologist. New York: Basic Books. 433 p.
White F. 1988. Party composition and dynamics in Pan paniscus. Int J Prim 9(3): 179-93.
White F. 1996. Comparative socio-ecology of Pan paniscus. In: McGrew WC, Marchant LF, Nishida T, editors. Great ape societies. Cambridge, England: Cambridge Univ Pr; p 29-41.
Whittier CA, Nutter FB, Stoskopf MK. 2001. Zoonotic disease concerns in primate field settings. In: The apes: challenges for the 21st century. Conference proceedings; 2000 May 10-13; Brookfield, IL. Chicago: Chicago Zoo Soc; p 232-37.
Wrangham RW. 2001. Moral decisions about wild chimpanzees. In: Beck BB, Stoinski TS, Hutchins M, Maple TL, Norton B, Rowan A, Stevens EF, Arluke A, editors. Great apes & humans: the ethics of coexistence. Washington DC: Smithsonian Inst Pr; p 230-244.
IMAGES
Pan paniscus Photo: Joris Jacobs |
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Pan paniscus Photo: Joris Jacobs |
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Pan paniscus Photo: Joris Jacobs |
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Pan paniscus Photo: Joris Jacobs |
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Pan paniscus Photo: Joris Jacobs |
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Pan paniscus Photo: Joris Jacobs |
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Pan paniscus Photo: Joris Jacobs |
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Pan paniscus Photo: Joris Jacobs |
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Pan paniscus Photo: Joris Jacobs |
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Pan paniscus Photo: Max Planck Institut |
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Pan paniscus Photo: Max Planck Institut |
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Pan paniscus Photo: Max Planck Institut |
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Pan paniscus Photo: Max Planck Institut |
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Pan paniscus Photo: Max Planck Institut |
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Pan paniscus Photo: Max Planck Institut |
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Pan paniscus Photo: Max Planck Institut |
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Pan paniscus Photo: Max Planck Institut |
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Pan paniscus Photo: Max Planck Institut |
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Pan paniscus Photo: Max Planck Institut |
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Pan paniscus Photo: Max Planck Institut |
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Pan paniscus Photo: Max Planck Institut |
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Pan paniscus Photo: Max Planck Institut |
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Pan paniscus Photo: Primates in Art & Illustration Collection |
Cite this page as: Cawthon Lang KA. 2010 December 1. Primate Factsheets: Bonobo (Pan paniscus) Conservation . <http://pin.primate.wisc.edu/factsheets/entry/bonobo/cons>. Authored December 1, 2010 by Kristina Cawthon Lang. Reviewed by Frans de Waal.
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