Lomami National Park: Difference between revisions
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* Key threats to bonobos are hunting and habitat loss due to expansion of subsistence farming. | * Key threats to bonobos are hunting and habitat loss due to expansion of subsistence farming. | ||
* Conservation activities have focused on biomonitoring, anti-poaching patrols, and community involvement. | * Conservation activities have focused on biomonitoring, anti-poaching patrols, and community involvement. | ||
| Line 48: | Line 44: | ||
= Ape status = | = Ape status = | ||
The Congolese Institute for Nature Conservation (ICCN) reported an estimated population of 9,500 individuals (5,800–13,700) in Lomami, including the surrounding buffer zone (IUCN & ICCN 2012). | The Congolese Institute for Nature Conservation (ICCN) reported an estimated population of 9,500 individuals (5,800–13,700) in Lomami, including the surrounding buffer zone ([[#R01106|IUCN & ICCN 2012]]). | ||
'''Table 2. Ape population estimates reported for Lomami National Park''' | '''Table 2. Ape population estimates reported for Lomami National Park''' | ||
| Line 119: | Line 115: | ||
!Implementing organization(s) | !Implementing organization(s) | ||
!Year of activity | !Year of activity | ||
|- | |- | ||
|2 Counter-wildlife crime | |2 Counter-wildlife crime | ||
| Line 131: | Line 121: | ||
|African Wildlife Foundation, Antwerp Zoo Foundation, ICCN | |African Wildlife Foundation, Antwerp Zoo Foundation, ICCN | ||
|Ongoing (2022) | |Ongoing (2022) | ||
|- | |||
|5 Protection & restoration | |||
|5.2 Legally protect ape habitat | |||
|The site was declared a National Park in 2016. | |||
| | |||
|2016-Ongoing (2026) | |||
|- | |- | ||
|7 Economic & other incentives | |7 Economic & other incentives | ||
| Line 240: | Line 236: | ||
= Exposure to climate change impacts = | = Exposure to climate change impacts = | ||
As part of a study on the exposure of African great ape sites to climate change impacts, Kiribou et al. | As part of a study on the exposure of African great ape sites to climate change impacts, [[#R02249|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. | ||
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 ( | 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 ([[#R02249|Kiribou et al. 2024]]). | ||
'''Table 8. Estimated past and projected climatological characteristics in Lomami National Park''' | '''Table 8. Estimated past and projected climatological characteristics in Lomami National Park''' | ||
| Line 365: | Line 361: | ||
= References = | = References = | ||
Batumike, R., Imani, G., Urom, C., & Cuni-Sanchez, A. (2021). Bushmeat hunting around Lomami National Park, Democratic Republic of the Congo. Oryx, 55(3), 421-431. doi:10.1017/S0030605319001017 | <span id="R01104"></span>Batumike, R., Imani, G., Urom, C., & Cuni-Sanchez, A. (2021). Bushmeat hunting around Lomami National Park, Democratic Republic of the Congo. Oryx, 55(3), 421-431. doi:10.1017/S0030605319001017 | ||
<span id="R01105"></span>Frankfurt Zoological Society (FZS). (n.d.). Lomami National Park. Online: https://fzs.org/en/projects/democratic-republic-of-the-congo/lomami-national-park/ | |||
<span id="R01106"></span>IUCN, & ICCN (2012). Bonobo (Pan paniscus): Conservation Strategy 2012–2022. Gland, Switzerland: IUCN/SSC Primate Specialist Group & Institut Congolais pour la Conservation de la Nature. [http://www.primate-sg.org/storage/pdf/Bonobo_Conservation_Strategy.pdf link] | |||
<span id="R02249"></span>Kiribou, R., Tehoda, P., Chukwu, O., Bempah, G., Kühl, H. S., Ferreira, J., …, & Heinicke, S. (2024). Exposure of African ape sites to climate change impacts. ''PLOS Climate'', 3(2), e0000345. [https://doi.org/10.1371/journal.pclm.0000345 doi:10.1371/journal.pclm.0000345] | |||
'''Page created by: '''APES Atlas Team''' Date:''' 2022-03-25 | '''Page created by: '''APES Atlas Team''' Date:''' 2022-03-25 | ||
Latest revision as of 17:53, 15 October 2026
Central Africa > Democratic Republic of the Congo > Lomami National Park
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Summary
- Bonobos (Pan paniscus) are present in Lomami National Park.
- It has been estimated that 9,500 individuals occur in the park and its buffer area.
- The bonobo population trend is unknown.
- The site has a total size of 8,879 km².
- Key threats to bonobos are hunting and habitat loss due to expansion of subsistence farming.
- Conservation activities have focused on biomonitoring, anti-poaching patrols, and community involvement.
Site characteristics
Lomami National Park is situated in the Democratic Republic of Congo, between the rivers Tshuapa, Lomami, and Lualaba (FZS). The park was established in 2016, and it covers an area of nearly 9,000 km² and has a buffer zone of approximately 20,000 km². The region is covered by dense tropical rainforests, swamp forests and savannas (Batumike et al. 2020). The park is home to several endangered and rare or endemic species, including bonobos, forest elephants, giant pangolins, hippos, okapis, Congo peafowl, the recently discovered dryas monkey, and the Lesula monkey, discovered in the park in 2012 (Batumike et al. 2020, FZS).
Table 1. Basic site information for Lomami National Park
| Species | Pan paniscus |
| Area | 8,879 km² |
| Coordinates | Lat: -1.329433 , Lon: 25.069388 |
| Type of site | Protected area (National Park) |
| Habitat types | Subtropical/tropical moist lowland forest, Subtropical/tropical swamp forest |
| Type of governance |
Types of sites Governance types Habitat types
Ape status
The Congolese Institute for Nature Conservation (ICCN) reported an estimated population of 9,500 individuals (5,800–13,700) in Lomami, including the surrounding buffer zone (IUCN & ICCN 2012).
Table 2. Ape population estimates reported for Lomami National Park
| 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 paniscus | Lomami National Park |
Sampling methods Analytical frameworks
Threats
Based on village surveys around the park, there is a misconception about hunting in the buffer zone, as villagers often believe that they are allowed to hunt any species in the buffer zone, including bonobos (Batumike et al. 2020).
Table 3. Threats to apes reported for Lomami National Park
| Category | Specific threats | Threat level | Description | Year of threat |
|---|---|---|---|---|
| 2 Agriculture & aquaculture | 2.1 Annual & perennial non-timber crops | Present (unknown severity) | Small-scale subsistence agriculture (cassava, maize and rice) (Batumike et al. 2020). | Ongoing (2020) |
| 5 Biological resource use | 5.1 Hunting & collecting terrestrial animals | High (more than 70% of population affected) | Hunting for subsistence, including bonobos and other species of conservation concern (Batumike et al. 2020). | Ongoing (2020) |
Conservation activities
In 2007, the first team set out to explore and document the region in and around the park. The data collected have been used to improve the protection of the park and gain a better understanding of the distribution of different species (FZS). In 2021, the ICCN and Frankfurt Zoological Society (FZS) signed a co-management agreement, which made FZS's Lomami Project leader the director of Lomami National Park.
Table 4. Conservation activities reported for Lomami National Park
| Category | Specific activity | Description | Implementing organization(s) | Year of activity |
|---|---|---|---|---|
| 2 Counter-wildlife crime | 2.3 Conduct regular anti-poaching patrols | Regular patrols conducted jointly by TL2 project staff (named after the rivers in the project area, Tshuapa, Lomami, and Lualaba) and Congolese Nature Conservation Institute (ICCN) rangers. During patrols, data on species diversity and distribution are also collected, as well as on the occurrence of illegal activities (FZS). | African Wildlife Foundation, Antwerp Zoo Foundation, ICCN | Ongoing (2022) |
| 5 Protection & restoration | 5.2 Legally protect ape habitat | The site was declared a National Park in 2016. | 2016-Ongoing (2026) | |
| 7 Economic & other incentives | 7.1 Provide monetary benefits to local communities for sustainably managing their forest and its wildlife (e.g., REDD, alternative income, employment) | The Lomami Conservation Project offers sustainable income opportunities and helps involve the communities in the park development (FZS). | Ongoing (2022) |
Challenges
Table 5. Challenges reported for Lomami National Park
| Challenges | Specific challenges | Source | Year(s) |
|---|---|---|---|
| Not reported |
Enablers
Table 6. Enablers reported for Lomami National Park
| Enablers | Specific enablers | Source | Year(s) |
|---|---|---|---|
| 1 Site management | |||
| 2 Resources and capacity | |||
| 3 Engaged community | |||
| 4 Institutional support | |||
| 5 Ecological context | |||
| 6 Safety and stability |
Research activities
In 2012, a new species of monkey, Cercopithecus lomamiensis, was discovered on the left bank of the Lomami River (FZS). The park harbours a remarkable diversity of mammals, and is also very rich in plant species- one new species of plant has also been found here, Xenostegia lomamiensis (FZS).
Documented behaviours
Table 7. Behaviours documented for Lomami National Park
| Category | Behavior | Observation type | Prevalence | Observation dates | Source | Habituation | Species | Comment |
|---|---|---|---|---|---|---|---|---|
| Not reported |
Exposure to climate change impacts
As part of a study on the exposure of African great ape sites to climate change impacts, 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.
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 (Kiribou et al. 2024).
Table 8. Estimated past and projected climatological characteristics in Lomami National Park
| 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] | 25.2 | 26.4 | 26.2 | 26.6 | 27.7 |
| Annual precipitation [mm] | 1856 | 1870 | 1866 | 1832 | 1957 |
| Max no. consecutive dry days (per year) | 9.8 | 15 | 15 | 17.4 | 13.8 |
| No. days with heavy precipitation (per year) | 6.9 | 9.6 | 8.5 | 9.9 | 12 |
Table 9. Projected exposure of apes to extreme climate impact events in Lomami National Park
| 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 | 15.5 | 0 | 13.5 | 0 | 16.5 | 0.01 | 28.5 | 0 |
| Drought | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
| Heatwave | 10 | 46.98 | 5 | 52.88 | 10.5 | 59.58 | 23 | 59.01 |
| River flood | 5 | 1.02 | 5.25 | 1.38 | 5 | 1.14 | 7.25 | 0.88 |
| Tropical cyclone | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
| Wildfire | 30 | 0.47 | 30 | 0.45 | 29 | 0.58 | 29 | 0.43 |
External links
References
Batumike, R., Imani, G., Urom, C., & Cuni-Sanchez, A. (2021). Bushmeat hunting around Lomami National Park, Democratic Republic of the Congo. Oryx, 55(3), 421-431. doi:10.1017/S0030605319001017
Frankfurt Zoological Society (FZS). (n.d.). Lomami National Park. Online: https://fzs.org/en/projects/democratic-republic-of-the-congo/lomami-national-park/
IUCN, & ICCN (2012). Bonobo (Pan paniscus): Conservation Strategy 2012–2022. Gland, Switzerland: IUCN/SSC Primate Specialist Group & Institut Congolais pour la Conservation de la Nature. link
Kiribou, R., Tehoda, P., Chukwu, O., Bempah, G., Kühl, H. S., Ferreira, J., …, & Heinicke, S. (2024). Exposure of African ape sites to climate change impacts. PLOS Climate, 3(2), e0000345. doi:10.1371/journal.pclm.0000345
Page created by: APES Atlas Team Date: 2022-03-25

