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[[Central Africa]] > [[Cameroon]] > [[Campo Ma'an National Park]]
[[East Africa]] > [[Rwanda]] > [[Rwanda Nationwide]]


'''[https://apesatlas-iucnapesportal-org.translate.goog/index.php/Campo_Ma'an_National_Park?_x_tr_sl=auto&_x_tr_tl=fr&_x_tr_hl=en&_x_tr_pto=wapp Français]''' | '''[https://apesatlas-iucnapesportal-org.translate.goog/index.php/Campo_Ma'an_National_Park?_x_tr_sl=auto&_x_tr_tl=pt&_x_tr_hl=en&_x_tr_pto=wapp Português]''' | '''[https://apesatlas-iucnapesportal-org.translate.goog/index.php/Campo_Ma'an_National_Park?_x_tr_sl=auto&_x_tr_tl=es&_x_tr_hl=en&_x_tr_pto=wapp Español]''' | '''[https://apesatlas-iucnapesportal-org.translate.goog/index.php/Campo_Ma'an_National_Park?_x_tr_sl=auto&_x_tr_tl=id&_x_tr_hl=en&_x_tr_pto=wapp Bahasa Indonesia]''' | '''[https://apesatlas-iucnapesportal-org.translate.goog/index.php/Campo_Ma'an_National_Park?_x_tr_sl=auto&_x_tr_tl=ms&_x_tr_hl=en&_x_tr_pto=wapp Melayu]'''
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__TOC__
__TOC__
= Summary =
= Summary =


<div style='float: right'>{{#display_map: height=190px | width=300px | scrollzoom=off | zoom=5 | layers=OpenStreetMap,OpenTopoMap|2.389597, 10.206030~[[Campo Ma'an National Park]]~''Pan troglodytes troglodytes'', ''Gorilla gorilla gorilla''}}</div>
<div style='float: right'>{{#display_map: height=190px | width=300px | scrollzoom=off | zoom=5 | layers=OpenStreetMap,OpenTopoMap|-1.991215, 29.949308~[[Rwanda Nationwide]]~''Gorilla beringei beringei'', ''Pan troglodytes schweinfurthii''}}</div>
* Central chimpanzees (''Pan troglodytes troglodytes'') and western lowland gorillas (''Gorilla gorilla gorilla'') are present in Campo Ma'an National Park.
* Rwanda is home to two species of great apes: the mountain gorilla (''Gorilla beringei beringei'') and the eastern chimpanzee (''Pan troglodytes schweinfurthii'').
* In 2020, it was estimated that 718 gorillas and chimpanzees inhabit the site.
* The estimated populations of great apes in Rwanda include 669 gorillas (CI: 623–759) in the Virunga Massif (Volcanoes National Park), 306 chimpanzees in Nyungwe National Park (as of 2009), and 28 individuals in Gishwati-Mukura National Park.
* The great ape population trend is decreasing.
* Gorilla population trend is increasing in Volcanoes National Park, chimpanzee trend numbers are increasing in Gishwati-Mukura National Park, whereas chimpanzee population trend is decreasing in Nyungwe National Park.
* The site has a total size of 2,641 km².
* The combined area of Rwanda’s great ape protected sites comprises Volcanoes National Park (160 km²), Nyungwe National Park (1,019 km²), and Gishwati-Mukura National Park (35.58 km²).
* Large infrastructure projects, extractives and agro-industries are putting enormous pressure on the park.
* The key threats remain habitat loss, poaching, logging, and mining.
* Conservation activities have focused on patrolling the area and habituation of gorillas to strengthen the potential for ecotourism.
* The conservation activities have mainly focused on ecotourism and research activities.
* Rwanda’s integrated conservation and tourism model has made it a leader in ape conservation in Africa.
= Site characteristics =


Rwanda’s conservation landscape includes three major protected areas relevant to great apes:


= Site characteristics =
• [[Volcanoes National Park]] (160 km²): Situated in the Virunga massif, it is globally renowned for its mountain gorilla population. The park is also home to golden monkeys and diverse montane ecosystems.
 
• [[Nyungwe National Park]] (1,019 km²): One of Africa’s largest montane rainforests, home to about 300 chimpanzees, 12 other primate species, and remarkable biodiversity.


Established in 2000, Campo Ma'an National Park is located in southwestern Cameroon, bordering Equatorial Guinea and the Atlantic Ocean. The vegetation consists largely of coastal evergreen rainforest. Several species of plants have beeen recently discovered, which may be endemic ([[#R00319|BirdLife International 2020]]). In addition to gorillas (''Gorilla gorilla'') and chimpanzees (''Pan troglodytes''), other mammals found in the park include forest elephants (''Loxodonta cyclotis''), and several species of primates, including mandrills (''Mandrillus sphinx''), and black colobus (''Colobus satanas''). The African manatee (''Trichechus senegalensis'') also occurs in the western part of the park. More than 165 species of fish have been recorded, of which four are endemic to Campo Ma'an. The park is also rich in reptiles (122 species recorded), and birds (200 species recorded in the site, and 100 species recorded in adjacent areas; [[#R00319|BirdLife International 2020]]). The park was designated as an Important Bird Area in 2001 ([[#R00319|BirdLife International 2020]]).Campo Ma’an National Park is surrounded by a buffer zone of several forest management units (Unités Techniques Opérationelles – UTOs), where commercial logging, agro-industrial expansion, and infrastructure projects have intensified since 2008, affecting wildlife abundance and connectivity ([[#R00327|Zo’obo Engolo et al. 2025]])
• [[Gishwati-Mukura National Park]] (35.58 km²): Rwanda’s newest national park, gazetted in 2015, comprising two forest fragments. It harbors around 30 chimpanzees, along with golden and L’Hoest’s monkeys.


'''Table 1. Basic site information for Campo Ma'an National Park'''
'''Table 1. Basic site information for Rwanda Nationwide'''
{| border="1" cellpadding="5" cellspacing="0" class="Site_characteristics-table"
{| border="1" cellpadding="5" cellspacing="0" class="Site_characteristics-table"
|Species
|Species
|''Pan troglodytes troglodytes'', ''Gorilla gorilla gorilla''
|''Gorilla beringei beringei'', ''Pan troglodytes schweinfurthii''
|-
|-
|Area
|Area
|2,641 km²
|26,338 km²
|-
|-
|Coordinates
|Coordinates
|Lat: 2.389597 , Lon:  10.206030
|Lat: -1.991215 , Lon:  29.949308
|-
|-
|Type of site
|Type of site
|Protected area (National Park)
|Nation
|-
|-
|Habitat types
|Habitat types
|Subtropical/tropical moist lowland forest, Wetlands (lakes, rivers, streams, bogs, marshes)
|Subtropical/tropical moist montane forest, Wetlands (lakes, rivers, streams, bogs, marshes), Rocky areas (inland cliffs, mountain peaks)
|-
|-
|Type of governance
|Type of governance
|Governance by government
|Governance by the government, Shared governance
|}
|}


[[Types of sites]] [[Governance types]] [[Habitat types]]  
[[Types of sites]] [[Governance types]] [[Habitat types]]  
= Ape status =
= Ape status =


Mountain gorillas in '''Volcanoes National Park''' number around 600, and the population trend is reported to be increasing. Chimpanzees in '''Nyungwe''' are estimated at around 300 individuals. Two habituated communities reside in the park: the Mayebe community (50–60 individuals) and the Cyamudongo community (35–40 individuals; [[#R01591|Moore et al. 2018a]]).
Meanwhile, '''Gishwati-Mukura''' holds about 30 individuals. The chimpanzee population in the Gishwati forest has increased in size—from 13 individuals in 2007, to 19 in 2010, and more recently, in 2019, chimpanzee trackers were able to identify 28 individuals ([[#R01568|Chancellor et al. 2020]]).


 
'''Table 2. Ape population estimates reported for Rwanda Nationwide'''
'''Table 2. Ape population estimates reported for Campo Ma'an National Park'''
{| border="1" cellpadding="5" cellspacing="0" class="Ape_status-table"
{| border="1" cellpadding="5" cellspacing="0" class="Ape_status-table"
!Species
!Species
Line 61: Line 66:
!A.P.E.S. database ID
!A.P.E.S. database ID
|-
|-
|''Pan troglodytes troglodytes'' & ''Gorilla gorilla gorilla''
|''Pan troglodytes schweinfurthii''
|2020
|2019
|
|
|
|
|
|
|718.0
|28.0
|Campo Ma'an National Park
|Gishwati Forest
|Line transects & recces
|Full count
|
|
|[[#R00327|Zo’obo Engolo et al. 2025]]
|[[#R01568|Chancellor et al. 2020]]
|
|
|
|
|-
|-
|''Pan troglodytes troglodytes'' & ''Gorilla gorilla gorilla''
|''Gorilla beringei beringei''
|2014
|2015-16
|
|
|
|
|
|
|1472.0
|669 (623-759)
|Campo Ma'an National Park
|Virunga massif (450 km²​)
|Line transects
|Genetic (dung/hair)
|
|Spatially explicit capture-recapture, Reconnaissance walk
|[[#R00323|N'Goran 2017]]
|[[#R02080|Granjon et al. 2020]]
|Combination of recces and mark-recapture; estimate for the entire population including gorillas in DRC and Uganda
|
|
|-
|''Gorilla beringei beringei''
|2010
|
|
|-
|''Pan troglodytes troglodytes''
|2014
|
|
|
|
|1.01 (0.71-1.42)
|480
|351 (250-495)
|Virunga massif (450 km²​)
|Campo Ma'an National Park, Dipikar (348.34 km²)
|Genetic (dung/hair)
|Line transects
|Count method
|Distance sampling with survey specific decay time
|[[#R02081|Gray et al. 2013]]
|[[#R00324|Nzooh Dongmo et al. 2015]]
|Recces; estimate for the entire population including gorillas in DRC and Uganda
|
|
|CMR0021
|-
|-
|''Gorilla gorilla gorilla''
|''Pan troglodytes schweinfurthii''
|2014
|2009-2010
|
|
|
|
|1.25 (0.70-2.23)
|436 (245-776)
|Campo Ma'an National Park, Dipikar (348.34 km²)
|Line transects
|Distance sampling with survey specific decay time
|[[#R00324|Nzooh Dongmo et al. 2015]]
|
|
|CMR0021
|19.0
|-
|Gishwati Forest Reserve
|''Pan troglodytes troglodytes'' & ''Gorilla gorilla gorilla''
|Genetic (dung/hair)
|2014
|
|
|[[#R01567|Chancellor et al. 2012]]
|
|
|1.99 (1.47-2.70)
|RWA0002
|694 (513-940)
|-
|Campo Ma'an National Park, Dipikar (348.34 km²)
|''Pan troglodytes schweinfurthii''
|Line transects
|2009
|Distance sampling with survey specific decay time
|[[#R00324|Nzooh Dongmo et al. 2015]]
|
|
|CMR0021
|-
|''Gorilla gorilla gorilla''
|2014
|
|
|
|
|0.16 (0.08-0.31)
|306.0
|369 (191-710)
|Nyungwe Forest National Park
|Campo Ma'an National Park, Nord (2,266.73 km²)
|Line transects
|Line transects
|Distance sampling with survey specific decay time
|[[#R00324|Nzooh Dongmo et al. 2015]]
|
|CMR0021
|-
|''Pan troglodytes troglodytes''
|2014
|
|
|WCS unpublished data, cited by Plumptre et al. 2010
|
|
|0.19 (0.11-0.34)
|440 (248-779)
|Campo Ma'an National Park, Nord (2,266.73 km²)
|Line transects
|Distance sampling with survey specific decay time
|[[#R00324|Nzooh Dongmo et al. 2015]]
|
|
|CMR0021
|-
|-
|''Gorilla gorilla gorilla''
|''Pan troglodytes schweinfurthii''
|2014
|2004-2005
|
|
|
|
|0.22 (0.14-0.33)
|1,000 (661-1,514)
|Campo Ma'an National Park and surroundings (4,609.6 km²)
|Line transects
|Distance sampling with survey specific decay time
|[[#R00324|Nzooh Dongmo et al. 2015]]
|
|
|CMR0021
|380.0
|-
|Nyungwe Forest National Park
|''Pan troglodytes troglodytes''
|Unknown
|2014
|
|
|WCS unpublished data, cited by Plumptre et al. 2010
|
|
|0.26 (0.20-0.35)
|1,220 (929-1,603)
|Campo Ma'an National Park and surroundings (4,609.6 km²)
|Line transects
|Distance sampling with survey specific decay time
|[[#R00324|Nzooh Dongmo et al. 2015]]
|
|
|CMR0021
|-
|-
|''Pan troglodytes troglodytes'' & ''Gorilla gorilla gorilla''
|''Gorilla beringei beringei''
|2014
|2003
|
|
|
|
|0.34 (0.21-0.55)
|778 (484-1,250)
|Campo Ma'an National Park, Nord (2,266.73 km²)
|Line transects
|Distance sampling with survey specific decay time
|[[#R00324|Nzooh Dongmo et al. 2015]]
|
|
|CMR0021
|380
|Virunga massif (450 km²​)
|Genetic (dung/hair)
|Count method
|Gray et al. 2003
|Recces; estimate for the entire population including gorillas in DRC and Uganda
|
|-
|-
|''Pan troglodytes troglodytes'' & ''Gorilla gorilla gorilla''
|''Gorilla beringei beringei''
|2014
|2000
|
|
|
|
|0.48 (0.38-0.60)
|2,199 (1,736-2,786)
|Campo Ma'an National Park and surroundings (4,609.6 km²)
|Line transects
|Distance sampling with survey specific decay time
|[[#R00324|Nzooh Dongmo et al. 2015]]
|
|
|CMR0021
|359-395
|Virunga massif (450 km²​)
|Other (type here)
|Count method
|[[#R01585|Kalpers et al. 2003]]
|Used regular ranger patrols to count nests of unhabituated groups and known number of gorillas from habituated groups; estimate for the entire population including gorillas in DRC and Uganda
|
|-
|-
|''Pan troglodytes troglodytes'' & ''Gorilla gorilla gorilla''
|''Gorilla beringei beringei''
|2008
|1989
|
|
|
|
|1039.0
|Campo Ma'an National Park
|Line transects
|
|
|[[#R00323|N'Goran 2017]]
|
|
|324
|Virunga massif (450 km²​)
|Reconnaissance walk
|Count method
|Sholley 1991
|Counted night nests; estimate for the entire population including gorillas in DRC and Uganda
|
|
|-
|-
|''Gorilla gorilla gorilla''
|''Gorilla beringei beringei''
|1997-2000
|1986
|
|
|
|
|0.20
|
|Campo forest
|Line transects
|
|[[#R00322|Matthews & Matthews 2004]]
|
|
|293
|Virunga massif (450 km²​)
|Reconnaissance walk
|Count method
|Vedder and Aveling 1986
|Estimate for the entire population including gorillas in DRC and Uganda
|
|
|-
|-
|''Pan troglodytes troglodytes''
|''Gorilla beringei beringei''
|1997-2000
|1981
|
|
|
|
|0.63-0.78
|
|
|Campo forest
|254
|Virunga massif (450 km²​)
|Line transects
|Line transects
|Count method
|[[#R02082|Aveling and Harcourt 1984]]
|Estimate for the entire population including gorillas in DRC and Uganda
|
|
|[[#R00322|Matthews & Matthews 2004]]
|-
|''Gorilla beringei beringei''
|1976-78
|
|
|
|
|-
|''Pan troglodytes troglodytes''
|1997-2000
|
|
|268
|Virunga massif (450 km²​)
|Other (type here)
|Count method
|[[#R02083|Weber and Vedder 1983]]
|Used recces to count direct sightings, count nests and used demographic information from monitored groups; estimate for the entire population including gorillas in DRC and Uganda
|
|
|0.8-1.0
|-
|''Gorilla beringei beringei''
|1971-73
|
|
|Ma'an forest
|Line transects
|
|
|[[#R00322|Matthews & Matthews 2004]]
|
|
|274
|Virunga massif (450 km²​)
|Reconnaissance walk
|Count method
|[[#R02084|Harcourt and Groom 1972]], [[#R02085|Groom 1973]]
|Used recces and nest counts; estimate for the entire population including gorillas in DRC and Uganda
|
|
|-
|-
|''Gorilla gorilla gorilla''
|''Gorilla beringei beringei''
|1997-2000
|1959-60
|
|
|
|
|
|
|
|Ma'an forest
|400-500
|Line transects
|Virunga massif (450 km²​)
|Reconnaissance walk
|
|
|[[#R00322|Matthews & Matthews 2004]]
|[[#R02086|Schaller 1963]]
|Gorilla density was too low to allow an estimation.
|Estimate for the entire population including gorillas in DRC and Uganda
|
|
|}
|}


[[Sampling methods]] [[Analytical frameworks]]  
[[Sampling methods]] [[Analytical frameworks]]  
= Threats =
= Threats =


Areas immediately surrounding the park are being, or have been, logged ([[#R00319|BirdLife International 2020]]). Large infrastructure projects, extractives and agro-industries are putting enormous pressure on the park. They include the Kribi industrial port complex, the Memve’ele Hydropower Dam, the Mount Mammelles iron ore exploration project, the rubber plantation of Hévécam and SOCAPALM oil palm plantations, and the construction of a railway terminal to transport iron ore to the Kribi seaport ([[#R00326|WWF 2018]]). There is a strong positive correlation between the number of development projects deployed near CMNP and the average number of poaching offences ([[#R00327|Zo’obo Engolo et al. 2025]]). [[#cite-Testperson-Muster-2026|Testperson & Muster (2026)]] report further pressure.
Great apes in Rwanda face a range of interlinked threats across their habitats. In [[Volcanoes National Park]], mountain gorillas were historically impacted by large-scale agricultural conversion, with about half of the park destroyed in the 1950s and 1960s (Weber, 1987, 1989; [[#R01586|Maekawa et al., 2013]]). Although intentional hunting for trophies and live animal trade has ceased, gorillas remain highly vulnerable to snares set for other wildlife ([[#R01599|Robbins et al., 2011]]). Diseases, including respiratory viruses, gastrointestinal parasites, measles, and outbreaks of Ebola and rabies in the wider region, continue to present a major threat ([[#R02306|Mazet et al., 2020]]; [[#R01582|Hassell et al., 2017]]; [[#R01595|Petrželková et al., 2021]], 2022). Human encroachment, small-scale logging, livestock grazing, fire, and invasive species further pressure gorilla habitat ([[#R01566|Bush, 2010]]; [[#R01583|Hoek et al., 2023]]; [[#R01607|Uzabaho et al., 2023]]).


'''Table 3. Threats to apes reported for Campo Ma'an National Park'''
In [[Nyungwe National Park]], chimpanzees are primarily threatened by snares set for other wildlife, which frequently cause accidental injury or death ([[#R01592|Moore et al., 2018b]]; Grueter, pers. comm. 2025). Although poaching levels are lower than in other regions, it remains persistent, with nearly 40,000 poaching-related incidents recorded between 2006 and 2015 ([[#R01592|Moore et al., 2018b]]). Mining activities, fires set to harvest honey, crop-raiding conflicts, and invasive species such as the fast-spreading liana Sericostachys contribute to long-term risks for both chimpanzees and their forest habitat ([[#R01597|Plumptre et al., 2002]]; [[#R01601|Scholte et al., 2010]]).
{| border="1" cellpadding="5" cellspacing="0" class="Threats-table"
!Category
!Specific threats
!Threat level
!Description
!Year of threat
|-
|2 Agriculture & aquaculture
|2.1.3 Industrial farming (including palm oil)
|High (more than 70% of population affected)
|The park faces growing pressure from a cluster of large-scale developments. The Kribi Deep Sea Port, Memve’élé and Ntem hydroelectric dams, HEVECAM and SOCAPALM plantations, the CAMVERT palm oil project, Sinosteel mining, and the planned Kribi-Mbalam railway all of which have contributed to rising poaching rates and habitat fragmentation ([[#R00327|Zo’obo Engolo et al. 2025]]). Expansion of palm oil plantations, since 2019 ([[#R00321|Djoko et al. 2022]]).
|2019-Ongoing (2025)
|-
|3 Energy production & mining
|3.2.1 Industrial mining
|High (more than 70% of population affected)
|The park faces growing pressure from a cluster of large-scale developments. The Kribi Deep Sea Port, Memve’élé and Ntem hydroelectric dams, HEVECAM and SOCAPALM plantations, the CAMVERT palm oil project, Sinosteel mining, and the planned Kribi-Mbalam railway all of which have contributed to rising poaching rates and habitat fragmentation ([[#R00327|Zo’obo Engolo et al. 2025]]).
|Ongoing (2020)
|-
|5 Biological resource use
|5.1 Hunting & collecting terrestrial animals
|Present (unknown severity)
|Hunting pressure is relatively high, but it decreased by more than 50% from 2008 to 2014 ([[#R00323|N'Goran 2017]]). There are also reports that poaching of mammals increased in the park between 2011 and 2020 ([[#R00327|Zo’obo Engolo et al. 2025]]).
|2008-Ongoing (2020)
|-
|5 Biological resource use
|5.3 Logging & wood harvesting
|Present (unknown severity)
|Logging activities in the forest management units reported ([[#R00321|Djoko et al. 2022]]).
|2019-Ongoing (2022)
|-
|7 Natural system modifications
|7.2 Dams & water management/use
|High (more than 70% of population affected)
|The park faces growing pressure from a cluster of large-scale developments. The Kribi Deep Sea Port, Memve’élé and Ntem hydroelectric dams, HEVECAM and SOCAPALM plantations, the CAMVERT palm oil project, Sinosteel mining, and the planned Kribi-Mbalam railway all of which have contributed to rising poaching rates and habitat fragmentation ([[#R00327|Zo’obo Engolo et al. 2025]]).
|Ongoing (2020)
|}


[[Threats]]  
In [[Gishwati-Mukura National Park]], chimpanzees are severely impacted by historical deforestation, with only a fraction of the forest remaining by the early 2000s (NASA Earth Observatory; [[#R01568|Chancellor et al., 2020]]). Ongoing pressures include illegal logging, agricultural expansion, and mining, which continue to degrade and fragment critical habitat for this small and isolated chimpanzee population ([[#R01568|Chancellor et al., 2020]]).


= Conservation activities =
= Conservation activities =
Rwanda has developed one of the most extensive great ape conservation programs in Africa, combining strict protection, community engagement, research, and health interventions. [[Volcanoes National Park]], home to the mountain gorilla, was first legally protected in 1925, making it Africa’s oldest national park ([[#R01585|Kalpers et al., 2003]]). Since then, a wide range of conservation measures have been implemented. These include long-term anti-poaching patrols and daily monitoring of habituated gorilla groups ([[#R01581|Harcourt, 1986]]; [[#R01603|Stewart & Sicotte, 2001a]]), snare removal, and the permanent presence of rangers, veterinarians, and researchers (Dian Fossey Gorilla Fund, 2025). Gorilla health interventions have been central, with the creation of Gorilla Doctors to monitor, treat, and vaccinate apes when necessary ([[#R02307|Morrison et al., 2021]]; [[#R01602|Spelman et al., 2013]]). Rules limiting tourist visitation time, enforcing minimum viewing distances, and requiring masks and gloves are in place to reduce disease transmission ([[#R01574|Gilardi et al., 2021]]). At the same time, conservation has emphasized sustainable community benefits, including tourism employment, cooperatives, and livestock distribution, helping transform former hunters into conservation allies ([[#R01573|Fossey, 1983]]; Rwanda Development Board, 2025). Landmark initiatives such as the Kwita Izina gorilla-naming ceremony and conservation education programs have further raised awareness locally and internationally ([[#R01590|McGuinness, 2014]]).
In [[Nyungwe National Park]], declared a national park in 2004, conservation has focused on protecting chimpanzees and other primates through regular anti-poaching patrols, snare removal, and habitat buffering (Grueter, pers. comm., 2025). Tourist projects such as chimpanzee trekking, canopy walks, and colobus monkey viewing generate both revenue and employment, reinforcing the park’s permanent conservation presence ([[#R01594|Nyungwe Forest National Park, 2025]]). Regulations on tourist contact—limiting visits to one hour and maintaining safe distances—mirror those applied in Volcanoes NP. Local communities also benefit from incentive programs such as employment to local people and alternative income opportunities, linking forest conservation with sustainable livelihoods (Grueter, pers. comm., 2025).
In [[Gishwati-Mukura National Park]], more recent interventions have combined law enforcement, education, and habitat restoration. Declared a national park in 2015 ([[#R01584|Inman & Ntoyinkama, 2020]]), the site has eco-guards patrolling against logging, charcoal production, and mining, while eco-clubs in local schools raise awareness among youth ([[#R01568|Chancellor et al., 2020]]). Long-term chimpanzee research, initiated in 2008, continues to ensure a permanent conservation presence and provides critical data for future management ([[#R01568|Chancellor et al., 2020]]). A central goal of past and ongoing initiatives has been restoring the forest corridor to Nyungwe, preserving gene flow between the two chimpanzee populations ([[#R01568|Chancellor et al., 2020]]).
= Challenges =
Conservation of Rwanda’s great apes is constrained by a suite of long-standing, interlinked challenges. In '''Volcanoes National Park''', large-scale habitat conversion (with more than half the park altered for agriculture and settlement in the mid-20th century) remain a legacy that complicates site management and community relations (Weber, 1987, 1989). Recurrent shortfalls in funding, equipment, infrastructure and specialist training limit the scope and effectiveness of conservation interventions, and more recently the COVID-19 pandemic caused sharp losses in tourism income, unemployment and gaps in monitoring and research — all of which weakened on-the-ground capacity and community incentives for conservation ([[#R01604|Stewart & Sicotte, 2001b]]; [[#R01574|Gilardi et al., 2021]]). '''Gishwati-Mukura''' faces acute legacy challenges from severe historical deforestation and fragmentation that left only small forest remnants; restoring connectivity, maintaining law enforcement against illegal grazing, logging and mining, and building long-term local stewardship and financing remain central hurdles for effective chimpanzee conservation there ([[#R01569|Chancellor et al., 2021]]; [[#R01584|Inman & Ntoyinkama, 2020]]). Taken together, these issues — historic land-use conflicts, constrained capacity and financing, pandemic shocks, and ongoing illegal resource use. Creating a conservation environment in which sustaining long-term protection, monitoring and community benefits for Rwanda’s mountain gorillas and chimpanzees requires continued investment in training, infrastructure, transboundary coordination and resilient funding mechanisms (Weber, 1987, 1989; [[#R01598|Refisch & Jenson, 2016]]; [[#R01574|Gilardi et al., 2021]]).
= Enablers =
Conservation of Rwanda’s great apes, namely the mountain gorillas in '''Volcanoes National Park''' and the chimpanzees in '''Nyungwe''' and '''Gishwati-Mukura National Parks''', has been facilitated by a strong set of enablers. Adaptive management strategies, such as targeted anti-poaching patrols, have been critical in addressing direct threats ([[#R01599|Robbins et al., 2011]]). Long-term monitoring and research since 1967 have provided a robust scientific foundation for conservation planning, supported by continuous funding and technical expertise from diverse partnerships at local, regional, and international levels ([[#R01599|Robbins et al., 2011]]). Local communities have also become key enablers, benefiting from tourism revenue-sharing schemes—5% of gorilla tourism income was directed to communities in 2005, later raised to 10% in 2017—which has improved livelihoods and fostered positive attitudes toward conservation ([[#R02308|Kalulu et al., 2016]]; [[#R02309|Snyman et al., 2023]]). These programs, alongside employment opportunities as rangers, porters, and guides, have strengthened local support and reduced conflict with the parks. At the institutional level, the Rwandan government has played a central role through strong leadership, policy support, and effective coordination via the Rwanda Development Board, complemented by transboundary cooperation under the Greater Virunga Transboundary Collaboration ([[#R01598|Refisch & Jenson, 2016]]). Stability in Rwanda’s political and socio-economic context since the early 2000s has further reinforced the enabling environment for conservation ([[#R01586|Maekawa et al., 2013]]). Together, these enablers illustrate how integrated governance, community engagement, research, and stability underpin successful great ape conservation in Rwanda.
= Research activities =
Research activities have played a central role in shaping the conservation of Rwanda’s great apes, providing the scientific foundation for effective management and protection. The world’s longest-running gorilla research program was initiated by Dian Fossey in [[Volcanoes National Park]] in 1967, and has continued through the [https://gorillafund.org/ Dian Fossey Gorilla Fund] in partnership with national and international institutions. This work has covered diverse themes, including gorilla ecology, behavior, physiology, ranging patterns, population dynamics, and threats, while also expanding since 2003 to monitor broader ecosystem components such as bamboo phenology, golden monkeys, birds, amphibians, mammals, and climate ([[#R01600|Roelke & Smith, 2010]]; [[#R01606|Tuyisingize et al., 2010]]; [[#R01605|Tuyisingize et al., 2022]]). Gorilla Doctors, founded in 1985, complements these efforts by conducting applied health research on gorilla populations. More recently, social science research around Volcanoes National Park has investigated local community dynamics and conservation engagement (Dian Fossey Gorilla Fund, n.d.).
In [[Nyungwe National Park]], long-term studies led by Grueter and colleagues since 2016 have examined the Mayebe chimpanzee community, focusing on dietary ecology, ranging decisions, cognitive adaptations, and responses to food scarcity in a thermally challenging, high-elevation habitat. Their work has revealed the importance of figs as staple foods, flexible travel strategies including use of human-made trails, and dynamic home range shifts in response to fruit availability, while also shedding light on socio-ecological drivers of female gregariousness and gut microbiome variation ([[#R01587|Matthews et al., 2019]]; [[#R01588|Matthews et al., 2020]]; [[#R01575|Green, Boruff, & Grueter, 2020]]; [[#R01576|Green, Boruff, Niyigaba, Ndikubwimana, & Grueter, 2020]]; [[#R01589|Matthews et al., 2021]]; [[#R01580|Grueter, Ridley, Kaplin, & Matthews, 2023]]).
Complementary research in [[Gishwati-Mukura National Park]] has been promoted through the Critical Ecosystem Partnership Fund, which emphasizes biodiversity assessments and the integration of conservation science into park management (Critical Ecosystem Partnership Fund [CEPF], 2015). Collectively, these diverse research initiatives underscore how rigorous and sustained scientific inquiry has provided the ecological and social knowledge base underpinning conservation of Rwanda’s great apes.
= Documented behaviours =
Documented behaviors of Rwanda’s great apes provide valuable insights into their ecology and cultural repertoire. In '''Volcanoes National Park''', mountain gorilla social, feeding, and ranging behaviors have been intensively studied since 1967, generating one of the most comprehensive long-term behavioral datasets for any primate species (Dian Fossey Gorilla Fund, n.d.). In '''Nyungwe National Park''', chimpanzees have demonstrated notable tool-use behaviors, including the use of sticks to extract honey from both underground nests of stingless bees and arboreal bee nests, highlighting their ecological adaptability and problem-solving skills (Grueter, al-Razi et al., unpublished; Grueter, Green et al., unpublished). Together, these documented behaviors not only deepen scientific understanding but also reinforce the importance of behavioral research for guiding conservation strategies.
= Exposure to climate change impacts =






'''Table 4. Conservation activities reported for Campo Ma'an National Park'''
= External links =
{| border="1" cellpadding="5" cellspacing="0" class="Conservation_activities-table"
 
!Category
[https://rdb.rw/ Rwanda Development Board (RDB)]  <br>
!Specific activity
[https://visitrwanda.com/tourism/ Visit Rwanda-Tourism]  <br>
!Description
[https://visitrwanda.com/destinations/volcanoes-national-park/ Visit Rwanda-Volcanoes National Park]  <br>
!Implementing organization(s)
[https://gorillafund.org/ Dian Fossey Gorilla Fund]  <br>
!Year of activity
[https://gorillafund.org/what-we-do/scientific-research/scientific-publications/ Scientific Publications]  <br>
|-
[https://www.nyungweforest.com/ Nyungwe Forest National Park - A Destination Guide] <br>
|2 Counter-wildlife crime
[https://www.africanparks.org/the-parks/nyungwe African Parks-Nyungwe National Park]  <br>
|2.3 Conduct regular anti-poaching patrols
[https://visitrwanda.com/destinations/nyungwe-national-park-2/ Visit Rwanda-Nyungwe National Park]
|Park guards conduct regular patrols to halt poaching and human encroachment ([[#R02023|WWF]], WWF 2008). ([[#cite-Testperson-Muster-2026|Testperson & Muster 2026]]).
[https://rwanda.wcs.org/ WCS Rwanda] <br>
|MINFOF (Campo Ma’an park team); WWF; AWF; local community patrols
[https://d29l0tur8ol1gj.cloudfront.net/sites/default/files/guidebook-gishwati-mukura-national-park.pdf Gishwati-Mukura National Park_Guide Book] <br>
|2008-Ongoing (2020)
[https://en.unesco.org/biosphere/africa/gishwati-mukura-landscape Gishwati-Mukura Landscape Biosphere Reserve UNESCO]  <br>
|-
[https://visitrwanda.com/destinations/gishwati-mukura-national-park-2/ Visit Rwanda – Gishwati-Mukura National Park]  <br>
|5 Protection & restoration
 
|5.2 Legally protect ape habitat
 
|The site is a National Park.
= References =
|MINFOF
 
|2000-Ongoing (2026)
<span id="R01566"></span>Bush, G. (2010). Conservation education and community-based approaches to conservation in Rwanda.
|-
 
|6 Species management
<span id="R01567"></span>Chancellor, R. L., Langergraber, K., Ramirez, S., Rundus, A. S., & Vigilant, L. (2012). Genetic Sampling of Unhabituated Chimpanzees (Pan troglodytes schweinfurthii) in Gishwati Forest Reserve, an Isolated Forest Fragment in Western Rwanda. ''International Journal of Primatology'', 33(2), 479-488. [https://doi.org/10.1007/s10764-012-9591-6 doi:10.1007/s10764-012-9591-6]
|6.1 Habituate primates to human presence to reduce stress from tourists/researchers
 
|[[#R02023|WWF]] supports a gorilla habituation programme. Gorilla Habituation Project in the southwest region of the National Park, as efforts to make gorillas tolerant to human presence for research and possibly ecotourism ([[#R00320|Collins 2022]]).
<span id="R01568"></span>Chancellor, R. L., Rundus, A. S., & Nyandwi, S. (2020). Long-term conservation challenges in Gishwati Forest, Rwanda. African Primates, 13(1), 15–30.
|WWF
 
|2011-Ongoing (2022)
<span id="R01569"></span>Chancellor, R., Rundus, A., Nyandwi, S., Nyiratuza, M., & Aimable, T. (2021). Community-based conservation and chimpanzee research in Gishwati Forest, Rwanda. American Journal of Primatology, 83(4), e23195. https://doi.org/10.1002/ajp.23195
|}
 
<span id="R01570"></span>Critical Ecosystem Partnership Fund. (2015). Guidebook to Gishwati-Mukura National Park. https://www.cepf.net/sites/default/files/guidebook-gishwati-mukura-national-park.pdf
 
<span id="R01571"></span>Dian Fossey Gorilla Fund. (n.d.-a). Scientific research. https://gorillafund.org/what-we-do/scientific-research/scientific-publications/
 
<span id="R01572"></span>Dian Fossey Gorilla Fund. (n.d.-b). What we do. https://gorillafund.org
 
<span id="R01573"></span>Fossey, D. (1983). Gorillas in the mist. Houghton Mifflin.
 
<span id="R01574"></span>Gilardi, K. V. K., Düx, A., Gillespie, T. R., Kalema-Zikusoka, G., Leendertz, F., Nze-Nkogue, C., Patrono, L. V., Raphael, J., Sulistyo, F., Syaluha, E. K., & Whittier, C. (2021). Best practice guidelines for health monitoring and disease control in great ape populations. IUCN SSC Primate Specialist Group / IUCN.
 
<span id="R01575"></span>Green, D. R., Boruff, B. J., & Grueter, C. C. (2020). Chimpanzees use human-made trails to traverse between resource patches. American Journal of Primatology, 82(2), e23065. https://doi.org/10.1002/ajp.23065


[[Conservation activities]]
<span id="R01576"></span>Green, D. R., Boruff, B. J., Niyigaba, P., Ndikubwimana, T., & Grueter, C. C. (2020). Chimpanzees adapt their ranging behavior in response to fruit scarcity in a montane forest environment. Primates, 61(3), 367–380. https://doi.org/10.1007/s10329-020-00789-2


= Challenges =
<span id="R01577"></span>Grueter, C. C. (2025). Personal communication.


<span id="R01578"></span>Grueter, C. C., al-Razi, H., Matthews, L., & Ridley, A. (n.d.). Tool use by chimpanzees in Nyungwe National Park, Rwanda: Honey extraction from underground bee nests [Unpublished manuscript].


<span id="R01579"></span>Grueter, C. C., Green, D. R., Boruff, B. J., & Matthews, L. (n.d.). Tool use by chimpanzees in Nyungwe National Park, Rwanda: Honey extraction from arboreal bee nests [Unpublished manuscript].


'''Table 5. Challenges reported for Campo Ma'an National Park'''
<span id="R01580"></span>Grueter, C. C., Ridley, A. R., Kaplin, B. A., & Matthews, L. J. (2023). Social and ecological drivers of female gregariousness in chimpanzees. Behavioral Ecology, 34(2), 291–302. https://doi.org/10.1093/beheco/arac109
{| border="1" cellpadding="5" cellspacing="0" class="Challenges-table"
!Challenges
!Specific challenges
!Source
!Year(s)
|-
|
|Not reported
|
|
|}


[[Challenges]]
<span id="R01581"></span>Harcourt, A. H. (1986). Gorilla conservation in the Virunga volcanoes. IUCN.


= Enablers =
<span id="R01582"></span>Hassell, J. M., Begon, M., Ward, M. J., & Fèvre, E. M. (2017). Urbanization and Disease Emergence: Dynamics at the Wildlife–Livestock–Human Interface. ''Trends in Ecology & Evolution'', 32(1), 55-67. [https://doi.org/10.1016/j.tree.2016.09.012 doi:10.1016/j.tree.2016.09.012]


<span id="R01583"></span>Hoek, R. van der, et al. (2023). Fire disturbance and gorilla habitat in Volcanoes National Park. Biological Conservation, 280, 109946.


<span id="R01584"></span>Inman, R., & Ntoyinkama, J. (2020). Rwanda’s Gishwati-Mukura National Park: Community-based conservation and restoration. Parks, 26(1), 103–114.


'''Table 6. Enablers reported for Campo Ma'an National Park'''
<span id="R01585"></span>Kalpers, J., Williamson, E. A., Robbins, M. M., & McNeilage, A. (2003). Virunga gorillas: Declining population or successful recovery? Oryx, 37(3), 316–328.
{| border="1" cellpadding="5" cellspacing="0" class="enabler-table"
!Enablers
!Specific enablers
!Source
!Year(s)
|-
|1 Site management
|
|
|
|-
|2 Resources and capacity
|2.6 External partnerships that add expertise or resources
|[[#R00320|Collins 2022]]
|Ongoing (2022)
|-
|3 Engaged community
|
|
|
|-
|4 Institutional support
|
|
|
|-
|5 Ecological context
|
|
|
|-
|6 Safety and stability
|
|
|
|}


[[Enablers]]
<span id="R01586"></span>Maekawa, A., et al. (2013). Human disturbance history and forest recovery in Volcanoes National Park. Journal of Tropical Forest Science, 25(2), 176–186.


= Research activities =
<span id="R01587"></span>Matthews, L. J., Ridley, A. R., Kaplin, B. A., & Grueter, C. C. (2019). Fallback foods and dietary seasonality in montane chimpanzees. International Journal of Primatology, 40(5), 631–655. https://doi.org/10.1007/s10764-019-00104-1


<span id="R01588"></span>Matthews, L. J., Ridley, A. R., Kaplin, B. A., & Grueter, C. C. (2020). Dietary flexibility in a montane chimpanzee community. American Journal of Primatology, 82(7), e23139. https://doi.org/10.1002/ajp.23139


<span id="R01589"></span>Matthews, L. J., Ridley, A. R., Kaplin, B. A., & Grueter, C. C. (2021). Fruit availability, estrous females, and party size dynamics in chimpanzees. Behavioral Ecology and Sociobiology, 75(3), 35. https://doi.org/10.1007/s00265-021-02965-5


<span id="R01590"></span>McGuinness, S. (2014). Kwita Izina: Rwanda’s gorilla naming ceremony as conservation education. Conservation Heritage-Turambe Report.


= Documented behaviours =
<span id="R01591"></span>Moore, J., Mulindahabi, F., Masozera, M., Nichols, J. D., & Plumptre, A. J. (2018a). Landscape-level conservation planning in the Albertine Rift: Using wildlife surveys to map threats. Conservation Biology, 32(2), 343–356.


<span id="R01592"></span>Moore, J. F., Mulindahabi, F., Masozera, M. K., Nichols, J. D., Hines, J. E., Turikunkiko, E., & Oli, M. K. (2018b). Are ranger patrols effective in reducing poaching-related threats within protected areas? Journal of Applied Ecology, 55(1), 99–107. https://doi.org/10.1111/1365-2664.12965


<span id="R01593"></span>NASA Earth Observatory. (2001). Rwanda’s disappearing Gishwati Forest. https://earthobservatory.nasa.gov


'''Table 7. Behaviours documented for Campo Ma'an National Park'''
<span id="R01594"></span>Nyungwe Forest National Park. (2025). Tourism activities. https://nyungweforestnationalpark.org
{| border="1" cellpadding="5" cellspacing="0" class="behaviours-table"
!Category
!Behavior
!Observation type
!Prevalence
!Observation dates
!Source
!Habituation
!Species
!Comment
|-
|
|Not reported
|
|
|
|
|
|
|
|}


[[Behaviours]]
<span id="R01595"></span>Petrželková, K. J., et al. (2021). Health risks for great apes from human respiratory pathogens. Emerging Infectious Diseases, 27(12), 2932–2941.


= Exposure to climate change impacts =
<span id="R01596"></span>Petrželková, K. J., et al. (2022). Viral disease threats to great apes in Central Africa. Primate Conservation, 36, 1–12.


As part of a study on the exposure of African great ape sites to climate change impacts, [[#R02169|Kiribou et al. (2024)]] extracted climate data and data on projected extreme climate impact events for the site. Climatological characteristics were derived from observation-based climate data provided by the Inter-Sectoral Impact Model Intercomparison Project (ISIMIP, www.isimip.org). Parameters were calculated as the average across each 30-year period. For 1981-2010, the EWEMBI dataset from ISIMIP2a was used. For the two future periods (2021-2050 and 2071-2099) ISIMIP2b climate data based on four CMIP5 global climate models were used. For future projections, two Representative Concentration Pathways (RCP) were used. RCP 2.6 is a scenario with strong mitigation measures in which global temperatures would likely rise below 2C. RCP 6.0 is a scenario with medium emissions in which global temperatures would likely rise up to 3C by 2100. For the number of days with heavy precipitation events, the 98th percentile of all precipitation days (>1mm/d) was calculated for the 1979-2013 reference period as a threshold for a heavy precipitation event. Then, for each year, the number of days above that threshold was derived. The figures on temperature and precipitation anomaly show the deviation from the mean temperature and mean precipitation for the 1979-2013 reference period.
<span id="R01597"></span>Plumptre, A. J., Masozera, M., Fashing, P. J., McNeilage, A., Ewango, C., Kaplin, B. A., & Liengola, I. (2002). Biodiversity Surveys of the Nyungwe Forest Reserve In S.W. Rwanda.WCS Working Paper No. 19. [https://web.archive.org/web/20120604053800/http://anthro.fullerton.edu/pfashing/publications/Biodiversity_surveys.pdf link]


The estimated exposure to future extreme climate impact events (crop failure, drought, river flood, wildfire, tropical cyclone, and heatwave) is based on a published dataset by Lange et al. 2020 derived from ISIMIP2b data. The same global climate models and RCPs as described above were used. Within each 30-year period, the number of years with an extreme event and the average proportion of the site affected were calculated ([[#R02169|Kiribou et al. 2024]]).
<span id="R01598"></span>Refisch, J., & Jenson, J. (2016). Transboundary collaboration in the Greater Virunga Landscape: From gorilla conservation to conflict-sensitive transboundary landscape management. In ''Governance, Natural Resources, and Post-Conflict Peacebuilding'' (pp. 825-842). Routledge. [https://doi.org/10.4324/9780203109793-39 doi:10.4324/9780203109793-39]


'''Table 8. Estimated past and projected climatological characteristics in Campo Ma'an National Park'''
<span id="R01599"></span>Robbins, M. M., Gray, M., Fawcett, K. A., Nutter, F. B., Uwingeli, P., Mburanumwe, I., …, & Robbins, A. M. (2011). Extreme Conservation Leads to Recovery of the Virunga Mountain Gorillas. ''PLoS ONE'', 6(6), e19788. [https://doi.org/10.1371/journal.pone.0019788 doi:10.1371/journal.pone.0019788]
{| border="1" cellpadding="5" cellspacing="0" class="clima-table"
!Value
!1981-2010
!2021-2050, RCP 2.6
!2021-2050, RCP 6.0
!2071-2099, RCP 2.6
!2071-2099, RCP 6.0
|-
|Mean temperature [C]
|25.1
|26.2
|26.1
|26.4
|27.5
|-
|Annual precipitation [mm]
|3002
|3094
|3126
|3183
|3222
|-
|Max no. consecutive dry days (per year)
|12.2
|6.8
|8.4
|5.9
|9.9
|-
|No. days with heavy precipitation (per year)
|7
|8.2
|8.9
|9.5
|11.4
|}


<span id="R01600"></span>Roelke, C. E., & Smith, T. B. (2010). Amphibian diversity in the Albertine Rift: Endemic species in Volcanoes National Park. African Journal of Ecology, 48(3), 729–737. https://doi.org/10.1111/j.1365-2028.2009.01166.x


'''Table 9. Projected exposure of apes to extreme climate impact events in Campo Ma'an National Park'''
<span id="R01601"></span>Scholte, P., Rugerinyange, L., Bizimungu, F., & Ruzigandekwe, F. (2010). Reaching consensus: Impact of the liana Sericostachys scandens on forest dynamics in Nyungwe National Park, Rwanda. Oryx, 44(3), 325–326.
{| border="1" cellpadding="5" cellspacing="0" class="clima2-table"
!Type
!No. of years with event (2021-2050, RCP 2.6)
!% of site exposed (2021-2050, RCP 2.6)
!No. of years with event (2021-2050, RCP 6.0)
!% of site exposed (2021-2050, RCP 6.0)
!No. of years with event (2070-2099, RCP 2.6)
!% of site exposed (2070-2099, RCP 2.6)
!No. of years with event (2070-2099, RCP 6.0)
!% of site exposed (2070-2099, RCP 6.0)
|-
|Crop failure
|5
|0.01
|4.5
|0.01
|5
|0.01
|21.5
|0.01
|-
|Drought
|0
|0
|0
|0
|0
|0
|0
|0
|-
|Heatwave
|8
|100
|7.5
|100
|11.5
|100
|17.5
|100
|-
|River flood
|2
|1.12
|2
|1.91
|1
|0.77
|4.5
|0.14
|-
|Tropical cyclone
|0
|0
|0
|0
|0
|0
|0
|0
|-
|Wildfire
|26.75
|0.15
|28
|0.21
|25.75
|0.14
|28
|0.23
|}


<span id="R01602"></span>Spelman, L. H., Gilardi, K., Lukasik-Braum, M., Kinani, J. F., & Mudakikwa, A. (2013). Respiratory disease in mountain gorillas: An emerging threat to great ape conservation. EcoHealth, 10(1), 27–34.


<div><ul><li style="display: inline-block; vertical-align: top;"> [[File:PrecipAnomaly_Campo-Ma_an_NP.png| 450px | thumb| none | Precipitation anomaly in Campo Ma'an National Park]] </li><li style="display: inline-block; vertical-align: top;"> [[File:TempAnomaly_Campo-Ma_an_NP.png | 450px | thumb| none | Temperature anomaly in Campo Ma'an National Park]] </li></ul></div>
<span id="R01603"></span>Stewart, K. J., & Sicotte, P. (2001a). Mountain gorillas: Three decades of research at Karisoke. Cambridge University Press.


= External links =
<span id="R01604"></span>Stewart, K. J., & Sicotte, P. (2001b). Primate conservation in Volcanoes National Park: Lessons learned. African Primates, 6(1–2), 21–26.


[[#R02023|Kudu-Zombo Programme]]
<span id="R01605"></span>Tuyisingize, D., Kaplin, B. A., & Grueter, C. C. (2022). Ecology and conservation of golden monkeys (Cercopithecus mitis kandti) in the Virunga Massif and Gishwati forest. Primates, 63(6), 487–499. https://doi.org/10.1007/s10329-022-00992-0


= References =
<span id="R01606"></span>Tuyisingize, D., Uwizeye, R., & Fischer, A. (2010). Small mammal endemism in Volcanoes National Park, Rwanda. Biodiversity and Conservation, 19(12), 3337–3352. https://doi.org/10.1007/s10531-010-9901-7


<span id="R00319"></span>BirdLife International. (2020). Important Bird Areas factsheet: Campo Ma'an complex. Retrieved November 25, 2020, from http://www.birdlife.org
<span id="R01607"></span>Uzabaho, E., et al. (2023). Invasive species management in Volcanoes National Park. African Journal of Ecology, 61(2), 123–134.


<span id="R00320"></span>Collins, E. (2022). Occupancy and activity of sympatric central chimpanzee (Pan troglodytes troglodytes) and western lowland gorilla (Gorilla gorilla gorilla) in a multi-use landscape, Campo Ma’an Conservation Area, Southern Cameroon [Master’s thesis, Concordia University]. Spectrum Research Repository. https://spectrum.library.concordia.ca/id/eprint/991723/
<span id="R01608"></span>Weber, A. W. (1987a). Ruhengeri and its resources: An environmental profile of the Ruhengeri Prefecture. ETMA/USAID.


<span id="R00321"></span>Djoko, I. B., Weladji, R. B., Granados, A., Paré, P., & Body, G. (2022). Fruit Availability Influences Forest Elephant Habitat Use in a Human Dominated Landscape, Campo-Ma’an, Southern Cameroon. ''Tropical Conservation Science'', 15, 1-12. [https://doi.org/10.1177/19400829221117053 doi:10.1177/19400829221117053]
<span id="R01609"></span>Weber, A. W. (1987b). Socioecology of the mountain gorilla [Doctoral dissertation, University of Wisconsin–Madison].


<span id="R00322"></span>Matthews, A., & Matthews, A. (2004). Survey of gorillas ( Gorilla gorilla gorilla ) and chimpanzees ( Pan troglodytes troglodytes ) in Southwestern Cameroon. ''Primates'', 45(1), 15-24. [https://doi.org/10.1007/s10329-003-0058-4 doi:10.1007/s10329-003-0058-4]
<span id="R01610"></span>Weber, A. W. (1989). Conservation and development on the Zaire–Nile Divide: An analysis of value conflicts and convergence in the management of Afromontane forests in Rwanda [Unpublished doctoral thesis]. University of Wisconsin–Madison.


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East Africa > Rwanda > Rwanda Nationwide

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Summary

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  • Rwanda is home to two species of great apes: the mountain gorilla (Gorilla beringei beringei) and the eastern chimpanzee (Pan troglodytes schweinfurthii).
  • The estimated populations of great apes in Rwanda include 669 gorillas (CI: 623–759) in the Virunga Massif (Volcanoes National Park), 306 chimpanzees in Nyungwe National Park (as of 2009), and 28 individuals in Gishwati-Mukura National Park.
  • Gorilla population trend is increasing in Volcanoes National Park, chimpanzee trend numbers are increasing in Gishwati-Mukura National Park, whereas chimpanzee population trend is decreasing in Nyungwe National Park.
  • The combined area of Rwanda’s great ape protected sites comprises Volcanoes National Park (160 km²), Nyungwe National Park (1,019 km²), and Gishwati-Mukura National Park (35.58 km²).
  • The key threats remain habitat loss, poaching, logging, and mining.
  • The conservation activities have mainly focused on ecotourism and research activities.
  • Rwanda’s integrated conservation and tourism model has made it a leader in ape conservation in Africa.

Site characteristics

Rwanda’s conservation landscape includes three major protected areas relevant to great apes:

• Volcanoes National Park (160 km²): Situated in the Virunga massif, it is globally renowned for its mountain gorilla population. The park is also home to golden monkeys and diverse montane ecosystems.

• Nyungwe National Park (1,019 km²): One of Africa’s largest montane rainforests, home to about 300 chimpanzees, 12 other primate species, and remarkable biodiversity.

• Gishwati-Mukura National Park (35.58 km²): Rwanda’s newest national park, gazetted in 2015, comprising two forest fragments. It harbors around 30 chimpanzees, along with golden and L’Hoest’s monkeys.

Table 1. Basic site information for Rwanda Nationwide

Species Gorilla beringei beringei, Pan troglodytes schweinfurthii
Area 26,338 km²
Coordinates Lat: -1.991215 , Lon: 29.949308
Type of site Nation
Habitat types Subtropical/tropical moist montane forest, Wetlands (lakes, rivers, streams, bogs, marshes), Rocky areas (inland cliffs, mountain peaks)
Type of governance Governance by the government, Shared governance

Types of sites Governance types Habitat types

Ape status

Mountain gorillas in Volcanoes National Park number around 600, and the population trend is reported to be increasing. Chimpanzees in Nyungwe are estimated at around 300 individuals. Two habituated communities reside in the park: the Mayebe community (50–60 individuals) and the Cyamudongo community (35–40 individuals; Moore et al. 2018a). Meanwhile, Gishwati-Mukura holds about 30 individuals. The chimpanzee population in the Gishwati forest has increased in size—from 13 individuals in 2007, to 19 in 2010, and more recently, in 2019, chimpanzee trackers were able to identify 28 individuals (Chancellor et al. 2020).

Table 2. Ape population estimates reported for Rwanda Nationwide

Species Year Occurrence Encounter or vistation rate (nests/km; ind/day) Density estimate [ind./ km²] (95% CI) Abundance estimate (95% CI) Survey area Sampling method Analytical framework Source Comments A.P.E.S. database ID
Pan troglodytes schweinfurthii 2019 28.0 Gishwati Forest Full count Chancellor et al. 2020
Gorilla beringei beringei 2015-16 669 (623-759) Virunga massif (450 km²​) Genetic (dung/hair) Spatially explicit capture-recapture, Reconnaissance walk Granjon et al. 2020 Combination of recces and mark-recapture; estimate for the entire population including gorillas in DRC and Uganda
Gorilla beringei beringei 2010 480 Virunga massif (450 km²​) Genetic (dung/hair) Count method Gray et al. 2013 Recces; estimate for the entire population including gorillas in DRC and Uganda
Pan troglodytes schweinfurthii 2009-2010 19.0 Gishwati Forest Reserve Genetic (dung/hair) Chancellor et al. 2012 RWA0002
Pan troglodytes schweinfurthii 2009 306.0 Nyungwe Forest National Park Line transects WCS unpublished data, cited by Plumptre et al. 2010
Pan troglodytes schweinfurthii 2004-2005 380.0 Nyungwe Forest National Park Unknown WCS unpublished data, cited by Plumptre et al. 2010
Gorilla beringei beringei 2003 380 Virunga massif (450 km²​) Genetic (dung/hair) Count method Gray et al. 2003 Recces; estimate for the entire population including gorillas in DRC and Uganda
Gorilla beringei beringei 2000 359-395 Virunga massif (450 km²​) Other (type here) Count method Kalpers et al. 2003 Used regular ranger patrols to count nests of unhabituated groups and known number of gorillas from habituated groups; estimate for the entire population including gorillas in DRC and Uganda
Gorilla beringei beringei 1989 324 Virunga massif (450 km²​) Reconnaissance walk Count method Sholley 1991 Counted night nests; estimate for the entire population including gorillas in DRC and Uganda
Gorilla beringei beringei 1986 293 Virunga massif (450 km²​) Reconnaissance walk Count method Vedder and Aveling 1986 Estimate for the entire population including gorillas in DRC and Uganda
Gorilla beringei beringei 1981 254 Virunga massif (450 km²​) Line transects Count method Aveling and Harcourt 1984 Estimate for the entire population including gorillas in DRC and Uganda
Gorilla beringei beringei 1976-78 268 Virunga massif (450 km²​) Other (type here) Count method Weber and Vedder 1983 Used recces to count direct sightings, count nests and used demographic information from monitored groups; estimate for the entire population including gorillas in DRC and Uganda
Gorilla beringei beringei 1971-73 274 Virunga massif (450 km²​) Reconnaissance walk Count method Harcourt and Groom 1972, Groom 1973 Used recces and nest counts; estimate for the entire population including gorillas in DRC and Uganda
Gorilla beringei beringei 1959-60 400-500 Virunga massif (450 km²​) Reconnaissance walk Schaller 1963 Estimate for the entire population including gorillas in DRC and Uganda

Sampling methods Analytical frameworks

Threats

Great apes in Rwanda face a range of interlinked threats across their habitats. In Volcanoes National Park, mountain gorillas were historically impacted by large-scale agricultural conversion, with about half of the park destroyed in the 1950s and 1960s (Weber, 1987, 1989; Maekawa et al., 2013). Although intentional hunting for trophies and live animal trade has ceased, gorillas remain highly vulnerable to snares set for other wildlife (Robbins et al., 2011). Diseases, including respiratory viruses, gastrointestinal parasites, measles, and outbreaks of Ebola and rabies in the wider region, continue to present a major threat (Mazet et al., 2020; Hassell et al., 2017; Petrželková et al., 2021, 2022). Human encroachment, small-scale logging, livestock grazing, fire, and invasive species further pressure gorilla habitat (Bush, 2010; Hoek et al., 2023; Uzabaho et al., 2023).

In Nyungwe National Park, chimpanzees are primarily threatened by snares set for other wildlife, which frequently cause accidental injury or death (Moore et al., 2018b; Grueter, pers. comm. 2025). Although poaching levels are lower than in other regions, it remains persistent, with nearly 40,000 poaching-related incidents recorded between 2006 and 2015 (Moore et al., 2018b). Mining activities, fires set to harvest honey, crop-raiding conflicts, and invasive species such as the fast-spreading liana Sericostachys contribute to long-term risks for both chimpanzees and their forest habitat (Plumptre et al., 2002; Scholte et al., 2010).

In Gishwati-Mukura National Park, chimpanzees are severely impacted by historical deforestation, with only a fraction of the forest remaining by the early 2000s (NASA Earth Observatory; Chancellor et al., 2020). Ongoing pressures include illegal logging, agricultural expansion, and mining, which continue to degrade and fragment critical habitat for this small and isolated chimpanzee population (Chancellor et al., 2020).

Conservation activities

Rwanda has developed one of the most extensive great ape conservation programs in Africa, combining strict protection, community engagement, research, and health interventions. Volcanoes National Park, home to the mountain gorilla, was first legally protected in 1925, making it Africa’s oldest national park (Kalpers et al., 2003). Since then, a wide range of conservation measures have been implemented. These include long-term anti-poaching patrols and daily monitoring of habituated gorilla groups (Harcourt, 1986; Stewart & Sicotte, 2001a), snare removal, and the permanent presence of rangers, veterinarians, and researchers (Dian Fossey Gorilla Fund, 2025). Gorilla health interventions have been central, with the creation of Gorilla Doctors to monitor, treat, and vaccinate apes when necessary (Morrison et al., 2021; Spelman et al., 2013). Rules limiting tourist visitation time, enforcing minimum viewing distances, and requiring masks and gloves are in place to reduce disease transmission (Gilardi et al., 2021). At the same time, conservation has emphasized sustainable community benefits, including tourism employment, cooperatives, and livestock distribution, helping transform former hunters into conservation allies (Fossey, 1983; Rwanda Development Board, 2025). Landmark initiatives such as the Kwita Izina gorilla-naming ceremony and conservation education programs have further raised awareness locally and internationally (McGuinness, 2014).

In Nyungwe National Park, declared a national park in 2004, conservation has focused on protecting chimpanzees and other primates through regular anti-poaching patrols, snare removal, and habitat buffering (Grueter, pers. comm., 2025). Tourist projects such as chimpanzee trekking, canopy walks, and colobus monkey viewing generate both revenue and employment, reinforcing the park’s permanent conservation presence (Nyungwe Forest National Park, 2025). Regulations on tourist contact—limiting visits to one hour and maintaining safe distances—mirror those applied in Volcanoes NP. Local communities also benefit from incentive programs such as employment to local people and alternative income opportunities, linking forest conservation with sustainable livelihoods (Grueter, pers. comm., 2025).

In Gishwati-Mukura National Park, more recent interventions have combined law enforcement, education, and habitat restoration. Declared a national park in 2015 (Inman & Ntoyinkama, 2020), the site has eco-guards patrolling against logging, charcoal production, and mining, while eco-clubs in local schools raise awareness among youth (Chancellor et al., 2020). Long-term chimpanzee research, initiated in 2008, continues to ensure a permanent conservation presence and provides critical data for future management (Chancellor et al., 2020). A central goal of past and ongoing initiatives has been restoring the forest corridor to Nyungwe, preserving gene flow between the two chimpanzee populations (Chancellor et al., 2020).

Challenges

Conservation of Rwanda’s great apes is constrained by a suite of long-standing, interlinked challenges. In Volcanoes National Park, large-scale habitat conversion (with more than half the park altered for agriculture and settlement in the mid-20th century) remain a legacy that complicates site management and community relations (Weber, 1987, 1989). Recurrent shortfalls in funding, equipment, infrastructure and specialist training limit the scope and effectiveness of conservation interventions, and more recently the COVID-19 pandemic caused sharp losses in tourism income, unemployment and gaps in monitoring and research — all of which weakened on-the-ground capacity and community incentives for conservation (Stewart & Sicotte, 2001b; Gilardi et al., 2021). Gishwati-Mukura faces acute legacy challenges from severe historical deforestation and fragmentation that left only small forest remnants; restoring connectivity, maintaining law enforcement against illegal grazing, logging and mining, and building long-term local stewardship and financing remain central hurdles for effective chimpanzee conservation there (Chancellor et al., 2021; Inman & Ntoyinkama, 2020). Taken together, these issues — historic land-use conflicts, constrained capacity and financing, pandemic shocks, and ongoing illegal resource use. Creating a conservation environment in which sustaining long-term protection, monitoring and community benefits for Rwanda’s mountain gorillas and chimpanzees requires continued investment in training, infrastructure, transboundary coordination and resilient funding mechanisms (Weber, 1987, 1989; Refisch & Jenson, 2016; Gilardi et al., 2021).

Enablers

Conservation of Rwanda’s great apes, namely the mountain gorillas in Volcanoes National Park and the chimpanzees in Nyungwe and Gishwati-Mukura National Parks, has been facilitated by a strong set of enablers. Adaptive management strategies, such as targeted anti-poaching patrols, have been critical in addressing direct threats (Robbins et al., 2011). Long-term monitoring and research since 1967 have provided a robust scientific foundation for conservation planning, supported by continuous funding and technical expertise from diverse partnerships at local, regional, and international levels (Robbins et al., 2011). Local communities have also become key enablers, benefiting from tourism revenue-sharing schemes—5% of gorilla tourism income was directed to communities in 2005, later raised to 10% in 2017—which has improved livelihoods and fostered positive attitudes toward conservation (Kalulu et al., 2016; Snyman et al., 2023). These programs, alongside employment opportunities as rangers, porters, and guides, have strengthened local support and reduced conflict with the parks. At the institutional level, the Rwandan government has played a central role through strong leadership, policy support, and effective coordination via the Rwanda Development Board, complemented by transboundary cooperation under the Greater Virunga Transboundary Collaboration (Refisch & Jenson, 2016). Stability in Rwanda’s political and socio-economic context since the early 2000s has further reinforced the enabling environment for conservation (Maekawa et al., 2013). Together, these enablers illustrate how integrated governance, community engagement, research, and stability underpin successful great ape conservation in Rwanda.

Research activities

Research activities have played a central role in shaping the conservation of Rwanda’s great apes, providing the scientific foundation for effective management and protection. The world’s longest-running gorilla research program was initiated by Dian Fossey in Volcanoes National Park in 1967, and has continued through the Dian Fossey Gorilla Fund in partnership with national and international institutions. This work has covered diverse themes, including gorilla ecology, behavior, physiology, ranging patterns, population dynamics, and threats, while also expanding since 2003 to monitor broader ecosystem components such as bamboo phenology, golden monkeys, birds, amphibians, mammals, and climate (Roelke & Smith, 2010; Tuyisingize et al., 2010; Tuyisingize et al., 2022). Gorilla Doctors, founded in 1985, complements these efforts by conducting applied health research on gorilla populations. More recently, social science research around Volcanoes National Park has investigated local community dynamics and conservation engagement (Dian Fossey Gorilla Fund, n.d.).

In Nyungwe National Park, long-term studies led by Grueter and colleagues since 2016 have examined the Mayebe chimpanzee community, focusing on dietary ecology, ranging decisions, cognitive adaptations, and responses to food scarcity in a thermally challenging, high-elevation habitat. Their work has revealed the importance of figs as staple foods, flexible travel strategies including use of human-made trails, and dynamic home range shifts in response to fruit availability, while also shedding light on socio-ecological drivers of female gregariousness and gut microbiome variation (Matthews et al., 2019; Matthews et al., 2020; Green, Boruff, & Grueter, 2020; Green, Boruff, Niyigaba, Ndikubwimana, & Grueter, 2020; Matthews et al., 2021; Grueter, Ridley, Kaplin, & Matthews, 2023).

Complementary research in Gishwati-Mukura National Park has been promoted through the Critical Ecosystem Partnership Fund, which emphasizes biodiversity assessments and the integration of conservation science into park management (Critical Ecosystem Partnership Fund [CEPF], 2015). Collectively, these diverse research initiatives underscore how rigorous and sustained scientific inquiry has provided the ecological and social knowledge base underpinning conservation of Rwanda’s great apes.


Documented behaviours

Documented behaviors of Rwanda’s great apes provide valuable insights into their ecology and cultural repertoire. In Volcanoes National Park, mountain gorilla social, feeding, and ranging behaviors have been intensively studied since 1967, generating one of the most comprehensive long-term behavioral datasets for any primate species (Dian Fossey Gorilla Fund, n.d.). In Nyungwe National Park, chimpanzees have demonstrated notable tool-use behaviors, including the use of sticks to extract honey from both underground nests of stingless bees and arboreal bee nests, highlighting their ecological adaptability and problem-solving skills (Grueter, al-Razi et al., unpublished; Grueter, Green et al., unpublished). Together, these documented behaviors not only deepen scientific understanding but also reinforce the importance of behavioral research for guiding conservation strategies.

Exposure to climate change impacts

External links

Rwanda Development Board (RDB)
Visit Rwanda-Tourism
Visit Rwanda-Volcanoes National Park
Dian Fossey Gorilla Fund
Scientific Publications
Nyungwe Forest National Park - A Destination Guide
African Parks-Nyungwe National Park
Visit Rwanda-Nyungwe National Park WCS Rwanda
Gishwati-Mukura National Park_Guide Book
Gishwati-Mukura Landscape Biosphere Reserve UNESCO
Visit Rwanda – Gishwati-Mukura National Park


References

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Chancellor, R. L., Rundus, A. S., & Nyandwi, S. (2020). Long-term conservation challenges in Gishwati Forest, Rwanda. African Primates, 13(1), 15–30.

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