Pan paniscus 

Scope: Global
Language: English

Translate page into:

Taxonomy [top]

Kingdom Phylum Class Order Family
Animalia Chordata Mammalia Primates Hominidae

Scientific Name: Pan paniscus Schwarz, 1929
Common Name(s):
English Bonobo, Dwarf Chimpazee, Gracile Chimpanzee, Pygmy Chimpanzee
French Bonobo
Spanish Bonobo
Taxonomic Source(s): Mittermeier, R.A., Rylands, A.B. and Wilson D.E. 2013. Handbook of the Mammals of the World: Volume 3 Primates. Lynx Edicions, Barcelona.
Taxonomic Notes:

The Bonobo is also known as the Gracile Chimpanzee; formerly it was known as Pygmy Chimpanzee and Dwarf Chimpanzee. Population genetics suggest that Bonobos have a stable population history (Eriksson et al. 2004, Schubert et al. 2013), and that gene flow between populations is constrained by the larger riverine barriers (although Bonobos regularly enter water, they do not swim).

Assessment Information [top]

Red List Category & Criteria: Endangered A4bcd ver 3.1
Year Published: 2016
Date Assessed: 2016-03-24
Assessor(s): Fruth, B., Hickey, J.R., André, C., Furuichi, T., Hart, J., Hart, T., Kuehl, H., Maisels, F., Nackoney, J., Reinartz, G., Sop, T., Thompson, J. & Williamson, E.A.
Reviewer(s): Mittermeier, R.A. & Rylands, A.B.
Contributor(s): African Wildlife Foundation, Benishay, J., Bila-Isia, I., Butynski, T.M., Coxe, S., Dupain, J., Eriksson, J., Guislain, P., Hashimoto, C., Hohmann, G., Hurley, M., Ilambu, O., Mulavwa, N., Ndunda, M., Omasombo, V., Peereboom, Z., Scherlis, J., Serckx, A., Steel, L., Stevens, J., Verhage, B., Vosper, A., Wildlife Conservation Society & World Wildlife Fund
Due to high levels of illegal hunting, and habitat destruction and degradation, Pan paniscus is estimated to have experienced a significant population reduction in the last 15–20 years and it is thought that this reduction will continue for the next 60 years. Currently, by far the greatest threat to the Bonobo's survival is poaching for the commercial bushmeat trade. It has been estimated that nine tons of bushmeat are extracted daily from a 50,000-km² conservation landscape within the Bonobo’s range. Not only is there is a massive demand for bushmeat stemming from the cities, but rebel factions and poorly-paid government soldiers add to that demand, at the same time facilitating the flow of guns and ammunition (Fruth et al. 2013). In some areas, local taboos against eating Bonobo meat still exist, but in others, these traditions are disintegrating due to changing cultural values and population movements. Stricter enforcement of wildlife laws and more effective management are urgently needed.

Habitat loss through deforestation and fragmentation ranks second. Much of the forest loss in this region is caused by slash-and-burn subsistence agriculture, which is most intense where human densities are high or growing. Logging and mining do not yet occur on an industrial scale in the Bonobo’s range, but in future, industrial agriculture is very likely to become a serious threat. Minimising the conversion of intact forest to human-dominated land uses, will be critical for the future survival of Bonobos. Countrywide factors contributing to the decline include the mobility of growing human populations, opening markets, commercial exploitation of natural resources and road construction. As in the past, the survival of Bonobos will be determined by the levels of poaching and forest loss—threats that have been shown to accompany rapid growth in human populations and political instability (Nackoney et al. 2014). Due to their slow life history and a generation time estimated to be 25 years, Bonobo populations cannot withstand high levels of offtake. The population decline over a three-generation (75 year) period from 2003 to 2078 is likely to exceed 50%, hence qualifying this taxon as Endangered under criterion A.

Previously published Red List assessments:

Geographic Range [top]

Range Description:

Pan paniscus has a discontinuous range in the low-lying central basin of Equatorial Africa, south of the Congo River. Its range extends from the Lualaba River in the east, to the Kasai/Sankuru rivers in the south, and to the west as far as the Congo River just 300 km north of Kinshasa (Manzano forest) and around Lake Tumba/Lake Mai-Ndombe (Tumba-Ledima Reserve). The potential geographic range is approximately 563,330 km²; however, only 28% (156,211 km²) of this area is suitable for Bonobos (Hickey et al. 2013). Four geographically-distinct Bonobo strongholds have been identified (IUCN and ICCN 2012):

  • The ‘northern block’ (Maringa-Lopori-Wamba) includes the Luo Scientific Reserve, the Lomako-Yokokala Faunal Reserve, and the Kokolopori Bonobo Reserve with community-level protection;
  • The ‘eastern block’ (Tshuapa-Lomami-Lualaba) includes the Sankuru Natural Reserve;
  • The ‘southern block’ (Salonga) – the 36,000-km² Salonga National Park (SNP) was the first protected area created that harbours bonobos;
  • The ‘western block’ (Lac Tumba-Lac Mai Ndombe) includes the Tumba-Lediima Natural Reserve.

Additional surveys are needed to better determine the species’ overall distribution and abundance.

Countries occurrence:
Congo, The Democratic Republic of the
Additional data:
Lower elevation limit (metres):300
Upper elevation limit (metres):700
Range Map:Click here to open the map viewer and explore range.

Population [top]

Population:The size of the Bonobo population is uncertain because only 30% of its historic range has been surveyed. Estimates from the four known Bonobo strongholds, based around protected areas, suggest a minimum population of 15,000–20,000 individuals (IUCN and ICCN 2012, IUCN SSC A.P.E.S. database 2016). Although Hickey et al. (2013) compiled and analysed all Bonobo survey data collected between 2003 and 2010, the survey coverage was too patchy to allow the total number of Bonobos to be estimated.

Sop et al. (in prep.) used spatial modelling to investigate trends in Bonobo nest encounter rates on recce and standard line transect surveys carried out in two different periods. Data were available from eight sites, covering a total area of 16,500 km². Site-specific change estimates were weighted according to population size, and then change in nest encounter rates between different years was used as a proxy for Bonobo population change. Rate of change was estimated using two approaches: site-level Generalized Linear Models (GLMs); and a simple exponential population change model (ExpM). Sop et al. estimated an annual decline of 5.95% with a total decline of 54.9% between 2003 and 2015 (95% confidence interval: -17.6% to +6.4% and -18% to +0.001% for the GLM and ExpM, respectively). Under the same conditions, the expected decline in abundance over one, two and three generations (25, 50 and 75 years respectively) would be 85.6%, 97.9% and 99.7%, respectively. However, not all sites experienced significant declines in Bonobo abundance. The Lokofa Sector of Salonga National Park, for example, has ecoguards deployed throughout and was the best protected of the eight sites in the analysis (WCS 2015). Although Sop et al.’s assessment incorporated data from both protected and non-protected areas, the total coverage was limited by data availability. In addition, the preliminary model had limitations with regard to the representativeness of sites and data availability, such as disproportionate sampling effort between years; and lack of data on seasonality, nest production, re-use and decay rates. If few nests are located and sample size is low, then precision tends to be poor, leading to weak detection of trends. Although a drop in abundance between the two time periods was detected, the small number of paired samples did not produce population sizes. The range-wide data required will eventually show areas considered to be suitable, but from which Bonobos are absent, and perhaps presence of Bonobos in areas not yet surveyed. Despite uncertainty around the modelled rate of decline, a strong negative trend is apparent in Sop et al.’s analysis. Even with an annual rate of decline of only 1%, total losses would exceed 50% over three generations, underscoring the need for monitoring of Bonobo populations and threats.

Current Population Trend:Decreasing
Additional data:
Continuing decline of mature individuals:Yes
Extreme fluctuations:NoPopulation severely fragmented:No
Extreme fluctuations in subpopulations:UnknownAll individuals in one subpopulation:No

Habitat and Ecology [top]

Habitat and Ecology:The geographic range of Pan paniscus is characterised by undulating terrain with elevations between 300 and 700 m asl and a humid climate (Fruth et al. 2013). Bonobos inhabit closed, moist, mixed, mature and secondary forests as well as forest-savannah mosaics (ibid.). In the eastern and southern parts of their range, Bonobos occupy a mosaic of moist tropical forest, dry forest, savannah woodland, marshy grassland and swamp forest, yet they also require access to relatively-undisturbed mature forests. If available, Bonobos prefer primary forests and seasonally-inundated swamp forests, foraging in small streams and breast-deep ponds (Narat 2014, Serckx 2014).

Bonobos are diurnal and semi-terrestrial. They live in multimale-multifemale, fission-fusion communities, usually made up of 30–80 individuals. A single community occupies a home range of 20–60 km², and there is extensive overlap between the ranges of different communities (Fruth et al. 2013). Bonobos are omnivorous; over 50% of their diet is comprised of fruits and seeds, which are supplemented with leaves, stems, shoots, pith, bark, flowers, truffles, fungus, and honey (Hohmann et al. 2006). They appear to be more dependent on terrestrial herbaceous vegetation, including aquatic plants, than chimpanzees. Bonobos have occasionally been documented hunting and eating vertebrates (e.g., duikers, primates; Hohmann and Fruth 2008) and invertebrates (e.g., termites, caterpillars; Kano 1992). Bonobos build new nests to sleep in each night and sometimes make day nests in trees at heights of 5–50 m (Fruth 1995). It has been reported that Bonobos also make ground nests (Kano 1983, Guislain and Reinartz pers. comm). Their role as seed dispersers is critical for forest regeneration (Tsuji et al. 2010, Beaune et al. 2013).

There is no birth season. Gestation is about eight months. Interbirth interval at Wamba (1976–1996) averages 4.8 years, and females average 0.18 offspring per year of their adult life. Physical maturation is slow with infants being weaned shortly before birth of the next offspring. Infant and juvenile mortality is low, with 73% of offspring surviving to age six (Furuichi et al. 1998). Females migrate aged 6–13 years, settling into a new community when they start cycling at 9–12 years. They produce their first offspring at 13–14 years of age (Furuichi et al. 2012). One generation is estimated to be 23–25 years (Myers Thompson 1997, T. Furuichi pers. comm. 2007, Langergraber et al. 2012).

Generation Length (years):23-25
Movement patterns:Not a Migrant

Use and Trade [top]

Use and Trade:

Killing or capture of Bonobos for any purpose is against national and international laws.

Threats [top]

Major Threat(s):

The major threats to Bonobos include: poaching (mainly for bushmeat and for some medicinal purposes); residue from civil warfare (availability of modern weaponry and ammunition; military-sanctioned hunting); human-induced habitat alteration (commercial logging and agriculture, traditional slash-and-burn agriculture, fallow land); human population growth and migration; and lack of education (insufficient awareness among urban and rural communities that hunting and eating Bonobos is unlawful). Bonobos reproduce slowly, and thus their populations are particularly susceptible to direct losses caused by humans. 

  1. Poaching: despite the fact that all killing, capture or consumption of great apes is illegal, poaching is the most direct and immediate threat to great apes in DRC. Although taboos against hunting Bonobos still exist in some regions, these taboos have become ineffective where poachers are not local. In other locations, transient and immigrant human populations with different cultural values have increased the frequency of hunting and eating of Bonobos. Poachers prefer large mammals, and since Bonobos are the largest primate in the region, they may be targeted along with ungulates and monkeys. Commercial poachers, aided by military and local administrations, are active even in legally-protected sites, such as Salonga National Park (SNP), Lomako-Yokokala Faunal Reserve, Tumba-Lediima Natural Reserve, Sankuru Natural Reserve, and the proposed Lomami National Park. The importance of these protected areas as significant reservoirs of Bonobos will be compromised rapidly if current levels of poaching continue. Between 2003 and 2006, Hart et al. (2008) recorded evidence of poaching in 51% of survey grids across SNP, with hunting pressure highest in the north and east. However, since then, investment in effective antipoaching measures appears to have protected at least the Lokofa Sector in the southern block of SNP, where Bonobo abundance remained stable between 2006 and 2015 (WCS 2015). Extrapolating from interview data gathered for a bushmeat survey conducted in the Lomami National Park (LNP) area in 2008, it was estimated that 270 Bonobos per year were consumed around Kindu, representing three Bonobos per 100 km² per year in the area investigated (Mirambo et al. 2014). Currently, this negative trend has been halted within the park through surveillance and collaboration with local communities (Hart and Hart 2011, 2015). The intake rate of orphaned Bonobos into the Lola ya Bonobo sanctuary may be viewed as another indicator of hunting pressure and/or anti-trafficking efforts. Hughes et al. (2011) estimated that 4.2 Chimpanzees (2.6–8.9 individuals) are removed from the wild whenever a single live infant is obtained as a by-product of a hunt. Considering that Bonobos are more social than Chimpanzees, the ratio of dead Bonobos per orphaned infant may be higher. Data compiled between 1994 and 2012 show a small but steady increase in the number of orphans entering the sanctuary, with two peaks each of six infants in 1997 and 2000 during the Congolese wars, and a peak of 16 individuals in 2004 after the implementation of peace and return to the regular use of rivers as major transport routes (ABC 2012). An influx of nine Bonobos in 2012 was also notably high, but arrivals decreased to two in 2015. While various explanations for lower intakes are possible (e.g., decline of Bonobos in the wild, or effective anti-poaching and anti-trafficking measures, or Bonobos being exported illegally), it is important to remember that the variation in such small numbers may be stochastic, rather than a real trend.
  2. Habitat loss: subsistence agriculture, commercial agriculture, logging and road construction all cause forest loss and fragmentation that reduces the usable (or ‘effective’) habitat available to Bonobos. Moreover, civil strife has been shown to exacerbate destruction and degradation of Bonobo habitat: in Luo Scientific Reserve and Iyondji Community Bonobo Reserve, primary forest loss in previously unfragmented core forests was over two times greater during a decade when conflict and war were predominant in the region (1990–2000) than during a relatively conflict-free period (2000–2010), when humans left their hiding in core forest areas and returned to their natal villages and farms within long-established agricultural complexes (Nackoney et al. 2014). However, as conflict recedes, large-scale commerce is expanding and industrial agriculture is likely to become a significant driver of forest loss. Oil palm is already being grown in what would otherwise be Bonobo habitat (Nackoney et al. 2012), and Africa is becoming the new frontier for oil-palm plantations, which offers excellent economic prospects in countries with appropriate rainfall, soil and temperature conditions (Rival and Levang 2014). A staggering 99.2% of the Bonobo’s range is suitable for oil palm (Wich et al. 2014), highlighting the enormous risk the palm-oil industry will pose unless sustainable management plans are developed and implemented to protect great apes and their habitats (IUCN SSC Primate Specialist Group 2014). It is worth noting that even though permits for prospection or resource extraction have already been granted, drilling for petroleum is unlikely to recommence in the near future, given the low price of crude oil on the international market. Although logging and mining do not yet occur on a large scale in Bonobo habitat, industrial extraction could become a serious threat in future. Minimising the conversion of intact forest in DRC to human-dominated land uses, will be critical for the survival of Bonobos, particularly when considering DRC’s high human population growth rate (2.45% in 2015; CIA 2015).
  3. Disease: infectious diseases are of particular concern in areas where Bonobos live in close proximity to human communities, or have been habituated to human observers for research or tourism purposes (Gilardi et al. 2015). Diseases that pose a risk to Bonobos include human-borne pathogens such as respiratory viruses, and natural pathogens such as Ebolavirus. Respiratory disease outbreaks were observed among Bonobos at Wamba when displaced people and soldiers were moving through the forest (Sakamaki et al. 2009), and human respiratory syncytial virus and Streptococcus pneumoniae co-infection has been detected at Malebo, where Bonobo habitat is surrounded by a particularly high human density (Leendertz pers. comm.). In 2014, a human outbreak of Ebola virus disease occurred in the Bonobo’s range. Considering their highly cohesive social structure, and high rates of physical contact, an Ebolavirus outbreak could devastate a Bonobo community. Despite a lack of scientific investigation of disease in wild Bonobos, these cases highlight the increasing need for health monitoring and disease contingency plans, as recommended by Gilardi et al. (2015).

Conservation Actions [top]

Conservation Actions:

Pan paniscus is listed on Appendix I of CITES and as Class A under the African Convention on the Conservation of Nature and Natural Resources. Bonobos are protected by national and international laws throughout their range, and the majority are found in national parks (IUCN SSC A.P.E.S. database 2016). However, most protected areas lack resources and suffer from poorly-controlled poaching, and enforcement is generally weak.

An IUCN and ICCN (2012) Bonobo conservation strategy ( outlines five intervention strategies with objectives and conservation actions centred on the Bonobo ‘strongholds’, which are to be implemented by 2022:

  1. Strengthening institutional capacity. One objective under this strategy is the creation of new protected areas. Since SNP was established in 1970, an additional 35,580 km² supporting Bonobos has been officially designated. The Iyondji Community Bonobo Reserve in the ‘northern block’ was created in 2012 (Sakamaki et al. 2012). The establishment of LNP, currently a provincial park with a ban on all hunting, will add 8,880 km² of protected habitat to the Bonobo’s range (Doumenge et al. 2015). Once LNP is officially gazetted, protected areas harbouring Bonobo populations will total more than 78,080 km². Protected areas, however, will not curtail poaching as long as law enforcement is ineffective, thus the objectives of eliminating poaching, monitoring and controlling the bushmeat trade, and eliminating the circulation of weapons and ammunition in protected areas are crucial. Considerable efforts have been made in SNP, with recent improvements in guard numbers, education and equipment. The government’s ‘Operation Bonobo’ aims to confiscate military weapons that have been in circulation since 2012, carry out joint FARDC and ICCN patrols, and liberate the parts of SNP under the control of poachers. A specially-trained ‘Corps en charge de la sécurisation des Parcs Nationaux’ will be in charge of anti-poaching in all national parks. However, law enforcement in the Bonobo’s range as a whole is still fragmentary, and conservation efforts are hampered by the vastness of the areas to be patrolled, as well as corruption and isolation, and persistent political and economic instability. NGOs and research projects with bilateral investment provide greater assurance of active and permanent on-the-ground enforcement, and are working to strengthen ICCN’s limited capacity throughout DRC.
  2. Consultation and collaboration with local actors. Here the main objective is to integrate conservation issues into national development plans, land-use and macro-zoning plans, and implement sustainable subsistence activities at key sites. In an attempt to transfer responsibility for managing natural resources to local communities, WWF began sensibilisation activities in the Lac Tumba and Salonga-Lukenie-Sankuru landscapes and around southern block of SNP, and assisted stakeholders to establish local development and conservation committees (Comités locaux de développement et de conservation). 
  3. Awareness building and lobbying. Objectives include developing a nationwide communications strategy, undertaking awareness-building activities at key sites, sensitising urban communities and private sector operators, and lobbying government administration at national and provincial levels. In 1995, USAID established the 25-year Central Africa Regional Programme for the Environment (CARPE) to increase local, national and regional capacity and participation in natural resource management, and strengthen conservation policy development and implementation to reduce biodiversity loss. Recently, CARPE established two distinct but interdependent projects: an Environmental Monitoring and Policy Support (EMAPS) project intended to boost the quality and scope of conservation policy-making, and forest monitoring, analysis and information dissemination; and CAFEC (see below; USAID 2014). Smaller organisations are conducting conservation education programmes in areas adjacent to Bonobo habitat as well as urban centres, such as Kinshasa or Kisangani, where demand for bushmeat is high. For example, Lola ya Bonobo in Kinshasa welcomes more than 20,000 visitors per annum, half of them school children. Such education-outreach activities can influence local attitudes to wildlife (ABC 2014).
  4. Research and monitoring activities. The primary objective here is to develop a clear framework for monitoring Bonobo populations and the threats to Bonobos, which is necessary to track changes in population size and distribution, to assess the level and location of threats, and ultimately to assess progress towards the Goal and Vision of the 2012 conservation strategy. The Central Africa Forest Ecosystems Conservation (CAFEC) project, and the SCAEMPS programme (Strengthening Central Africa Environmental Management and Policy Support) were established under CARPE. CAFEC supports the sustainable management of targeted forest landscapes, which include most of the landscapes where Bonobos occur, and involves targeted, site-based activities. SCAEMPS is a regional ‘quality control’ programme, ensuring that standardised, state of the art methods of monitoring wildlife, law enforcement (such as SMART, and livelihoods and governance are used across CARPE landscapes, and that databases are established to store the data collected. Supported by CARPE and other donors, ICCN and international NGOs have implemented surveys in about 40% of SNP. A three-year co-management agreement for the future monitoring and management of SNP was signed in 2015, focusing on the education, training and support of guards. Development of cost-efficient methods for biomonitoring (camera traps, drones) is underway. Development of a disease prevention plan to minimise human-Bonobo disease transmission, and establish an early detection mechanism and an emergency intervention plan to address potentially catastrophic disease outbreaks is not yet underway.
  5. Sustainable funding. Here, the objective is to evaluate funding needs for Bonobo conservation and create sustainable sources of funding. In the last 10 years, government donors (EU, KfW, USAID) have provided considerable conservation finance to support biodiversity conservation, park management, education or other developmental aid, rather than species-specific activities. While Bonobos will benefit from general support, a number of smaller donors (Arcus Foundation, Beneficia Foundation, USFWS, zoological gardens) are sponsoring the smaller NGOs and distinct projects focused on Bonobo conservation. Monetary support has slowly increased over time; however, the extent to which Bonobo populations outside protected areas is benefitting needs to be assessed. Fortunately, the Bonobo population does not need to be reinforced with individuals bred in captivity. In 2009 and 2011, Lola ya Bonobo, where intake rates and breeding have led to spatial constraints, released rehabilitated Bonobos back into the wild. The released individuals adapted easily to their new environment, became fully independent and reproduced successfully. Despite this success and the repopulation of a small area of former Bonobo habitat, reintroduction of great apes is controversial and often viewed as a mechanism for managing sanctuary populations (ABC 2014, C. André pers. comm.). Even more contentious are the potential ramifications for resident wild Bonobos, despite careful planning and selection of the site, and diligent preparation of the individual Bonobos released following IUCN guidelines for the reintroduction of great apes (Beck et al. 2007).

In sum, for protection of Bonobos to be effective, commercial poaching must be halted, intensification rather than expansion of local agriculture must be supported, and local industries must be actively persuaded to support rather than subvert conservation objectives. The most urgent conservation measures needed are those that enhance Bonobo survival in situ: effective law enforcement; long-term project presence on the ground; population monitoring; and education at all levels of society.

Errata [top]

Errata reason: This is an errata version of the 2016 assessment to correct some minor typos and grammatical errors in the Threats and Conservation Actions sections.

Classifications [top]

1. Forest -> 1.6. Forest - Subtropical/Tropical Moist Lowland
suitability:Suitable season:resident major importance:Yes
1. Forest -> 1.8. Forest - Subtropical/Tropical Swamp
suitability:Suitable season:resident major importance:Yes
1. Land/water protection -> 1.1. Site/area protection
1. Land/water protection -> 1.2. Resource & habitat protection
2. Land/water management -> 2.1. Site/area management
4. Education & awareness -> 4.1. Formal education
4. Education & awareness -> 4.2. Training
5. Law & policy -> 5.3. Private sector standards & codes
5. Law & policy -> 5.4. Compliance and enforcement -> 5.4.2. National level

In-Place Research, Monitoring and Planning
  Action Recovery plan:Yes
  Systematic monitoring scheme:No
In-Place Land/Water Protection and Management
  Conservation sites identified:Yes, over entire range
  Occur in at least one PA:Yes
  Percentage of population protected by PAs (0-100):71-80
  Area based regional management plan:Yes
  Invasive species control or prevention:Not Applicable
In-Place Species Management
  Harvest management plan:No
  Successfully reintroduced or introduced beningly:Yes
In-Place Education
  Subject to recent education and awareness programmes:Yes
  Included in international legislation:Yes
  Subject to any international management/trade controls:Yes
1. Residential & commercial development -> 1.1. Housing & urban areas
♦ timing:Ongoing ♦ scope:Minority (<50%) ♦ severity:Negligible declines ⇒ Impact score:Low Impact: 4 
→ Stresses
  • 1. Ecosystem stresses -> 1.1. Ecosystem conversion
  • 1. Ecosystem stresses -> 1.2. Ecosystem degradation

11. Climate change & severe weather -> 11.1. Habitat shifting & alteration
♦ timing:Ongoing ♦ scope:Whole (>90%) ♦ severity:Slow, Significant Declines ⇒ Impact score:Medium Impact: 7 
→ Stresses
  • 1. Ecosystem stresses -> 1.3. Indirect ecosystem effects

2. Agriculture & aquaculture -> 2.1. Annual & perennial non-timber crops -> 2.1.1. Shifting agriculture
♦ timing:Ongoing ♦ scope:Majority (50-90%) ♦ severity:Rapid Declines ⇒ Impact score:Medium Impact: 7 
→ Stresses
  • 1. Ecosystem stresses -> 1.1. Ecosystem conversion
  • 1. Ecosystem stresses -> 1.2. Ecosystem degradation

2. Agriculture & aquaculture -> 2.1. Annual & perennial non-timber crops -> 2.1.2. Small-holder farming
♦ timing:Ongoing ♦ scope:Majority (50-90%) ♦ severity:Slow, Significant Declines ⇒ Impact score:Medium Impact: 6 
→ Stresses
  • 1. Ecosystem stresses -> 1.1. Ecosystem conversion
  • 1. Ecosystem stresses -> 1.2. Ecosystem degradation

2. Agriculture & aquaculture -> 2.1. Annual & perennial non-timber crops -> 2.1.3. Agro-industry farming
♦ timing:Ongoing ♦ scope:Minority (<50%) ♦ severity:Very Rapid Declines ⇒ Impact score:Medium Impact: 7 
→ Stresses
  • 1. Ecosystem stresses -> 1.1. Ecosystem conversion
  • 1. Ecosystem stresses -> 1.2. Ecosystem degradation

2. Agriculture & aquaculture -> 2.3. Livestock farming & ranching -> 2.3.2. Small-holder grazing, ranching or farming
♦ timing:Ongoing ♦ scope:Minority (<50%) ♦ severity:Unknown ⇒ Impact score:Unknown 
→ Stresses
  • 1. Ecosystem stresses -> 1.1. Ecosystem conversion
  • 1. Ecosystem stresses -> 1.2. Ecosystem degradation

2. Agriculture & aquaculture -> 2.3. Livestock farming & ranching -> 2.3.3. Agro-industry grazing, ranching or farming
♦ timing:Ongoing ♦ scope:Minority (<50%) ♦ severity:Rapid Declines ⇒ Impact score:Medium Impact: 6 
→ Stresses
  • 1. Ecosystem stresses -> 1.1. Ecosystem conversion
  • 1. Ecosystem stresses -> 1.2. Ecosystem degradation

3. Energy production & mining -> 3.2. Mining & quarrying
♦ timing:Future ♦ scope:Minority (<50%) ♦ severity:Rapid Declines ⇒ Impact score:Low Impact: 4 
→ Stresses
  • 1. Ecosystem stresses -> 1.1. Ecosystem conversion
  • 1. Ecosystem stresses -> 1.2. Ecosystem degradation

5. Biological resource use -> 5.1. Hunting & trapping terrestrial animals -> 5.1.1. Intentional use (species is the target)
♦ timing:Ongoing ♦ scope:Majority (50-90%) ♦ severity:Very Rapid Declines ⇒ Impact score:High Impact: 8 
→ Stresses
  • 2. Species Stresses -> 2.1. Species mortality
  • 2. Species Stresses -> 2.2. Species disturbance

5. Biological resource use -> 5.1. Hunting & trapping terrestrial animals -> 5.1.2. Unintentional effects (species is not the target)
♦ timing:Ongoing ♦ scope:Minority (<50%) ♦ severity:Very Rapid Declines ⇒ Impact score:Medium Impact: 7 
→ Stresses
  • 2. Species Stresses -> 2.1. Species mortality
  • 2. Species Stresses -> 2.2. Species disturbance

5. Biological resource use -> 5.3. Logging & wood harvesting -> 5.3.3. Unintentional effects: (subsistence/small scale) [harvest]
♦ timing:Ongoing ♦ scope:Majority (50-90%) ♦ severity:Negligible declines ⇒ Impact score:Low Impact: 5 
→ Stresses
  • 1. Ecosystem stresses -> 1.1. Ecosystem conversion
  • 1. Ecosystem stresses -> 1.2. Ecosystem degradation

5. Biological resource use -> 5.3. Logging & wood harvesting -> 5.3.4. Unintentional effects: (large scale) [harvest]
♦ timing:Ongoing ♦ scope:Minority (<50%) ♦ severity:Slow, Significant Declines ⇒ Impact score:Low Impact: 5 
→ Stresses
  • 1. Ecosystem stresses -> 1.1. Ecosystem conversion
  • 1. Ecosystem stresses -> 1.2. Ecosystem degradation
  • 2. Species Stresses -> 2.2. Species disturbance

6. Human intrusions & disturbance -> 6.2. War, civil unrest & military exercises
♦ timing:Past, Likely to Return ♦ scope:Majority (50-90%) ♦ severity:Rapid Declines ⇒ Impact score:Past Impact 
→ Stresses
  • 2. Species Stresses -> 2.2. Species disturbance

6. Human intrusions & disturbance -> 6.3. Work & other activities
♦ timing:Ongoing ♦ scope:Minority (<50%) ♦ severity:Slow, Significant Declines ⇒ Impact score:Low Impact: 5 
→ Stresses
  • 2. Species Stresses -> 2.2. Species disturbance

8. Invasive and other problematic species, genes & diseases -> 8.5. Viral/prion-induced diseases -> 8.5.1. Unspecified species
♦ timing:Ongoing ♦ scope:Minority (<50%) ♦ severity:Very Rapid Declines ⇒ Impact score:Medium Impact: 7 
→ Stresses
  • 2. Species Stresses -> 2.1. Species mortality
  • 2. Species Stresses -> 2.3. Indirect species effects -> 2.3.7. Reduced reproductive success

1. Research -> 1.2. Population size, distribution & trends
1. Research -> 1.5. Threats
1. Research -> 1.6. Actions
2. Conservation Planning -> 2.1. Species Action/Recovery Plan
3. Monitoring -> 3.1. Population trends
3. Monitoring -> 3.2. Harvest level trends
3. Monitoring -> 3.3. Trade trends
3. Monitoring -> 3.4. Habitat trends

Bibliography [top]

ABC. 2012. Etat des lieux alarmant des arrivées d’orphelins bonobos au sanctuaire Lola ya Bonobo de l’ABC. Les Amis des Bonobos au Congo (ABC), Kinshasa.

ABC. 2014. Rapport d’activités des Amis des Bonobos du Congo au Ministère de l’Environnement, Conservation de la Nature et Développement Durable. Les Amis des Bonobos au Congo (ABC), Kinshasa.

Beaune, D., Bretagnolle, F., Bollache, L., Bourson, C., Hohmann, G. and Fruth, B. 2013. Ecological services performed by the bonobo (Pan paniscus): seed dispersal effectiveness in tropical forest. Journal of Tropical Ecology 29: 367–380.

Beck, B., Walkup, K., Rodrigues, M., Unwin, S., Travis, D. and Stoinski, T. 2007. Best Practice Guidelines for the Re-introduction of Great Apes. IUCN SSC Primate Specialist Group, Gland, Switzerland.

CIA. 2015. The World Factbook. Washington, D.C. Available at: (Accessed: 15 April).

Doumenge, C., Palla, F., Scholte, P., Hiol Hiol, F. and Larzillière, A. (eds). 2015. Aires protégées d’Afrique centrale – État 2015. pp. 256. Observatoire des Forêts d’Afrique Centrale (OFAC), Kinshasa, République Démocratique du Congo et Yaoundé, Cameroun.

Eriksson, J., Hohmann, G., Boesch, C. and Vigilant, L. 2004. Rivers influence the population genetic structure of bonobos (Pan paniscus). Molecular Ecology 13: 3425-3435.

Fruth, B. 1995. Nests and Nest Groups in Wild Bonobos (Pan paniscus): Ecological and Behavioural Correlates. Aachen: Verlag Shaker.

Fruth, B., Williamson, E.A. and Richardson, M.C. 2013. Bonobo Pan paniscus. In: R.A. Mittermeier, A.B. Rylands and D.E. Wilson (eds), Handbook of the Mammals of the World Volume 3: Primates, pp. 853–854. Lynx Edicions, Barcelona, Spain.

Furuichi, T., Idani, G., Ihobe, H., Hashimoto, C., Tashiro, T., Sakamaki, T., Mulavwa, M.N., Yangozene, K. and Kuroda, S. 2012. Long-term studies on wild bonobos at Wamba, Luo Scientific Reserve, D. R. Congo: towards the understanding of female life history in a male-philopatric species. In: Kappeler, P. and Watts, D. (eds), Long-term Field Studies of Primates, pp. 413–433. Springer-Verlag Berlin, Heidelberg.

Furuichi, T., Idani, G., Ihobe, H., Kuroda, S., Kitamura, K., Mori, A. Enomoto, T., Okayasu, N., Hashimoto, C. and Kano, T. 1998. Population dynamics of wild bonobos (Pan paniscus) at Wamba. International Journal of Primatology 19: 1029–1043.

Gilardi, K.V., Gillespie, T.R., Leendertz, F.H., Macfie, E.J., Travis, D.A., Whittier, C.A. and Williamson, E.A. 2015. Best Practice Guidelines for Health Monitoring and Disease Control in Great Ape Populations. IUCN SSC Primate Specialist Group, Gland, Switzerland.

Hart, J.A., Grossmann, F., Vosper, A. and Ilanga, J. 2008. Human hunting and its impact on the bonobo in Salonga National Park, D.R. Congo. In: The Bonobos: Behaviour, Ecology, And Conservation. In: Furuichi, T. and Thompson, J. (eds), The Bonobos: Behavior, Ecology and Conservation, pp. 245–271. Springer, New York.

Hart, T. and Hart, J. 2011. Breaking the bushmeat cycle in Congo: a good news story. SWARA 1: 16–19.

Hart, T. and Hart, J. 2015. Annual report to the Arcus Foundation. Annex 1.1.A: Comparison of bushmeat traffic into Kindu in 2009 and 2015. Lukuru Foundation, Kinshasa.

Hickey, J.P., Nackoney, J., Nibbelink, N.P., Blake, S., Bonyenge, A., Coxe, S., Dupain, J., Emetshu, M., Furuichi, T., Grossmann, F., Guislain, P., Hart, J., Hashimoto, C., Ikembelo, B., Ilambu, O., Inogwabini, B., Liengola, I., Lokasola, A., Lushimba, A., Maisels, F., Masselink, J., Mbenzo, V., Mulavwa, N., Naky, P., Ndunda, N., Nkumu, P., Omasombo, V., Reinartz, G., Rose, R., Sakamaki, T., Strindberg, S., Takemoto, H., Vosper, A. and Kuehl, H. 2013. Human proximity and habitat fragmentation are key drivers of the rangewide bonobo distribution. Biodiversity and Conservation 22: 3085–3104.

Hickey, J.R, Carroll, J.P. and Nibbelink, N.P. 2012. Applying landscape metrics to characterize potential habitat of bonobos (Pan paniscus) in the Maringa-Lopori-Wamba landscape, Democratic Republic of Congo. International Journal of Primatology 33: 381–400.

Hohmann, G. and Fruth, B. 2008. New records on prey capture and meat eating by bonobos at Lui Kotale, Salonga National Park, Democratic Republic of Congo. Folia Primatologica 79: 103–110.

Hohmann, G., Fowler, A., Sommer, V. and Ortmann, S. 2006. Frugivory and gregariousness of Salonga bonobos and Gashaka chimpanzees: the influence of abundance and nutritional quality of fruit. In: Hohmann, G., Robbins, M.M. and Boesch, C. (eds), Feeding Ecology in Apes and Other Primates, pp. 123–159. Cambridge University Press, Cambridge, U.K.

Hughes, N., Rosen, N., Gretsky, N. and Sommer, V. 2011. Will the Nigeria-Cameroon chimpanzee go extinct? Models derived from intake rates of ape sanctuaries. In: V. Sommer, and C. Ross (eds), Primates of Gashaka: Socioecology and Conservation in Nigeria’s Biodiversity Hotspot, pp. 545–575. Springer, New York.

IUCN. 2016. The IUCN Red List of Threatened Species. Version 2016-2. Available at: (Accessed: 04 September 2016).

IUCN. 2016. The IUCN Red List of Threatened Species. Version 2016-3. Available at: (Accessed: 07 December 2016).

IUCN and ICCN. 2012. Bonobo (Pan paniscus): Conservation Strategy 2012–2022. IUCN/SSC Primate Specialist Group and Institut Congolais pour la Conservation de la Nature, Gland, Switzerland.

IUCN SSC Primate Specialist Group. 2014. Industrial oil palm expansion in great ape habitat in Africa. A policy statement from the Section on Great Apes (SGA) of the IUCN SSC Primate Specialist Group. Available at:

James, R., Washington, R. and Rowell, D.P. 2013. Implications of global warming for the climate of African rainforests. Philosophical Transactions of the Royal Society B: Biological Sciences 368: 20120298.

Junker, J., Blake, S., Boesch, C., Campbell, G., du Toit, L., Duvall, C., Ekobo, A., Etoga, G., Galat-Luong, A., Gamys, J., Ganas-Swaray, J., Gatti, S., Ghiurghi, A., Granier, N., Hart, J., Head, J., Herbinger, I., Hicks, T.C., Huijbregts, B., Imong, I.S., Kumpel, N., Lahm, S., Lindsell, J., Maisels, F., McLennan, M., Martinez, L., Morgan, B., Morgan, D., Mulindahabi, F., Mundry, R., N'Goran K.P., Normand, E., Ntongho, A., Okon, D.T., Petre, C.A., Plumptre, A., Rainey, H., Regnaut, S., Sanz, C., Stokes, E., Tondossama, A., Tranquilli, S., Sunderland-Groves, J., Walsh, P., Warren Y., Williamson, E.A. and Kuehl, H.S. 2012. Recent decline in suitable environmental conditions for African great apes. Diversity and Distributions 18: 1077–1091.

Kano, T. 1983. An ecological study of the pygmy chimpanzees (Pan paniscus) of Yalosidi, Republic of Zaire. International Journal of Primatology 4: 1–31.

Kano, T. 1992. The Last Ape: Pygmy Chimpanzee Behavior and Ecology. Stanford University Press, Stanford, CA.

Korstjens, A.H., Lehmann, J. and Dunbar, R.I.M. 2010. Resting time as an ecological constraint on primate biogeography. Animal Behaviour 79: 361–374.

Langergraber, K.E., Prüfer, K., Rowney, C., Boesch, C., Crockford, C., Fawcett, K., Inoue, E., Inoue-Muruyama, M., Mitani, J.C., Muller, M.N., Robbins, M.M., Schubert, G., Stoinski, T.S., Viola, B., Watts, D., Wittig, R.M., Wrangham, R.W., Zuberbühler, K., Pääbo, S. and Vigilant, L. 2012. Generation times in wild chimpanzees and gorillas suggest earlier divergence times in great ape and human evolution. Proceedings of the National Academy of Sciences 109: 15716–15721.

Lehmann, J., Korstjens, A.H. and Dunbar, R.I.M. 2010. Apes in a changing world – the effects of global warming on the behaviour and distribution of African apes. Journal of Biogeography 37: 2217–2231.

Lewis, S.L., Sonke, B., Sunderland, T., Begne, S.K., Lopez-Gonzalez, G. et al. 2013. Above-ground biomass and structure of 260 African tropical forests. Philosophical Transactions of the Royal Society B-Biological Sciences 368: 20120295.

Mirambo, M., Hart, J.A., Mbey, J. and Hart, T.B. 2014. Distribution, abondance et conservation de bonobo (Pan paniscus) dans le Parc National de la Lomami et sa zone périphérique. First International Conference on Biodiversity in the Congo Basin, University of Kisangani.

Myers Thompson, J.A. 1997. The history, taxonomy and ecology of the bonobo (Pan paniscus) with a first description of a wild population living in a forest/savanna mosaic habitat. Unpublished thesis. University of Oxford, England.

Nackoney, J. and Williams, D. 2012. Conservation prioritization and planning with limited wildlife data in a Congo Basin forest landscape: assessing human threats and vulnerability to land use change. Journal of Conservation Planning 8: 25–44.

Nackoney, J., Molinario, G., Potapov, P., Turubanova, S., Hansen, M.C. and Furuichi, T. 2014. Impacts of civil conflict on primary forest habitat in northern Democratic Republic of the Congo, 1990–2010. Biological Conservation 170: 321–328.

Narat, V. 2014. Interactions bonobos-habitats-humains: habituation, écologie, santé et conservation. Ecole Doctorale Sciences de la Nature et de l’Homme, Musée National d'Histoire Naturelle.

Rival, A. and Levang, P. 2014. Palms of Controversies: Oil Palm and Development Challenges. CIFOR, Bogor, Indonesia.

Ryan, S.J. and Walsh, P.D. 2011. Consequences of non-intervention for infectious disease in African great apes. PLoS One 6: e29030.

Sakamaki, T., Kasalevo, P., Bokamba, M. B. and Bongoli, L. 2012. Iyondji Community Bonobo Reserve: a recently established reserve in the Democratic Republic of Congo. Pan Africa News 19: 16–19.

Sakamaki, T., Mulavwa, M. and Furuichi, T. 2009. Flu-like epidemics in wild bonobos (Pan paniscus) at Wamba, the Luo Scientific Reserve, Democratic Republic of Congo. Pan Africa News 16: 1–4.

Schubert, G., Vigilant, L., Boesch, C., Klenke, R., Langergraber, K.E., Mundry, R., Surbeck, M. and Hohmann, G. 2013. Co-residence between males and their mothers and grandmothers is more frequent in bonobos than chimpanzees. PLoS One 8(12): e83870.

Serckx, A. 2014. Eco-ethology of a population of bonobos (Pan paniscus) living in the western forest-savannah mosaics of the Democratic Republic of Congo. Département des Sciences et Gestion de l’Environnement, Université de Liège.

Sop, T., Mundry, R., Colleen, S. and Kühl, H.S. 2016. Report on estimated trends in abundance of bonobos (Pan paniscus).

Tsuji, Y., Yangozene, K. and Sakamaki, T. 2010. Estimation of seed dispersal distance by the bonobo, Pan paniscus, in a tropical forest in Democratic Republic of Congo. Journal of Tropical Ecology 26: 115–118.

WCS. 2015. Survey of the Lokofa Block of the Salonga National Park: preliminary report. Wildlife Conservation Society, Kinshasa, DRC.

Wich, S.A., Garcia-Ulloa, J., Kühl, H.S., Humle, T., Lee, J.S. and Koh, L.P. 2014. Will oil palm's homecoming spell doom for Africa's great apes? Current Biology 24: 1659–1663.

Citation: Fruth, B., Hickey, J.R., André, C., Furuichi, T., Hart, J., Hart, T., Kuehl, H., Maisels, F., Nackoney, J., Reinartz, G., Sop, T., Thompson, J. & Williamson, E.A. 2016. Pan paniscus. In: (errata version published in 2016). The IUCN Red List of Threatened Species 2016: e.T15932A102331567. . Downloaded on 22 June 2018.
Disclaimer: To make use of this information, please check the <Terms of Use>.
Feedback: If you see any errors or have any questions or suggestions on what is shown on this page, please provide us with feedback so that we can correct or extend the information provided