Difference between revisions of "Bafing"

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   3) Keywords must be taken from the list of permitted words, or added to the list of permitted keywords. A link to the keyword list page is found adjacent  
 
   3) Keywords must be taken from the list of permitted words, or added to the list of permitted keywords. A link to the keyword list page is found adjacent  
 
     to the relevant table or keyword list. This ensures that the same keyword always refers to the same concept, e.g. Everybody uses "Industrial mining",  
 
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     rather than several keywords such as "Industrial mining", "Large-scale mining", and "Mining".  
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     rather than several keywords such as "Industrial mining", "Large-scale mining", and "Mining".[[File: Map_MLI_BafingBR.png | 400px | thumb| right | Bafing  (Mali) © A.P.E.S. Wiki Team]]
 
-->
 
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<!-- Please add information for this site -->
 
<!-- Please add information for this site -->
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= Summary =  <!-- An overview of the site, with a one sentence overview of each of the following sections. can include a site map -->
 
= Summary =  <!-- An overview of the site, with a one sentence overview of each of the following sections. can include a site map -->
 
+
<div style="float: right">
* Western chimpanzees ([https://www.iucnredlist.org/species/15935/17989872 ''Pan troglodytes verus'']) are present in Bafing.  
+
{{#display_map: height=240px | width=320px | scrollzoom=off | zoom=7 | layers= OpenStreetMap, OpenTopoMap
 +
|12.90, -10.58~[[Bafing]]~Western Chimpanzee
 +
}}
 +
</div>
 +
* Western chimpanzees (''Pan troglodytes verus'') are present in Bafing.  
 
* It has been estimated that between 417-1,408 individuals occurred in the site in 1993.  
 
* It has been estimated that between 417-1,408 individuals occurred in the site in 1993.  
 
* The chimpanzee population trend is unknown.  
 
* The chimpanzee population trend is unknown.  
Line 20: Line 24:
 
* Key threats to chimpanzees is habitat degradation due to subsistence farming.  
 
* Key threats to chimpanzees is habitat degradation due to subsistence farming.  
 
* No conservation activities were reported for Bafing.
 
* No conservation activities were reported for Bafing.
* Hottest and driest place in which western chimpanzees exist (Kortlandt 1983). Chimpanzees do not seem to be restricted to riverine forest, but are spread widely through the soudanien woodland.
+
* Hottest and driest place in which western chimpanzees exist. Chimpanzees do not seem to be restricted to riverine forest, but are spread widely through woodland.
 
 
  
 
= Site characteristics = <!-- A paragraph summary of physical and geographic aspects of the site, and a table of key information -->
 
= Site characteristics = <!-- A paragraph summary of physical and geographic aspects of the site, and a table of key information -->
 +
[[File:MLI_Bafing_1.jpg|400px|thumb|right|Bafing (Mali) © E.Terrade]]
  
Bafing is situated in southern Mali. The current status of the site is not known. This site is 5000 km² (World Database on Protected Areas 2019). Woodlands dominate most of the landscape. During his survey of south-western Mali, Moore (1985) regularly observed buffalo ''Syncerus caffer'', roan '' Hippotragus equinus'', hartebeest '' Alcelaphus buselaphus'', and warthog '' Phacochoerus africanus''. Sayer (1977) encountered giant eland ''Tragelaphus derbianus'' and giraffe ''Giraffa camelopardalis'' in this area. Lion ''Panthera leo'', leopard ''Panthera pardus'', and African wild dog ''Lycaon pictus'' also probably occur at very low densities (Moore 1985). The current state of biodiversity is not known. Although this is the hottest and driest place in which western chimpanzees are known to exist (Kortlandt 1983), chimpanzees at this site do not seem to be restricted to riverine forest, but are spread widely through the soudanien woodland (Moore 1985).
+
Bafing is situated in southern Mali. The current status of the site is not known. This site is 5000 km² (World Database on Protected Areas 2019). Woodlands dominate most of the landscape. During his survey of south-western Mali, Moore (1985) regularly observed buffalo ''Syncerus caffer'', roan '' Hippotragus equinus'', hartebeest '' Alcelaphus buselaphus'', and warthog '' Phacochoerus africanus''. Sayer (1977) encountered giant eland ''Tragelaphus derbianus'' and giraffe ''Giraffa camelopardalis'' in this area. Lion ''Panthera leo'', leopard ''Panthera pardus'', and African wild dog ''Lycaon pictus'' also probably occur at very low densities (Moore 1985). The current state of biodiversity is not known. Although this is the hottest and driest place in which western chimpanzees are known to exist (Kortlandt 1983), chimpanzees at this site do not seem to be restricted to riverine forest, but are spread widely through the woodland (Moore 1985).
 
 
  
'''Table 1: Basic site information for Bafing'''
+
'''Table 1. Basic site information for Bafing'''
 
{| border="1" cellpadding="5" cellspacing="0" class="basic-information"
 
{| border="1" cellpadding="5" cellspacing="0" class="basic-information"
 
|Area            <!-- Please include units: km2/ha e.g 200ha    -->
 
|Area            <!-- Please include units: km2/ha e.g 200ha    -->
Line 34: Line 37:
 
|-
 
|-
 
|Coordinates
 
|Coordinates
|12.69 N, -10.34 W
+
|12.90, -10.58
 
|-
 
|-
 
|Designation      <!-- National Park, Nature Reserve, etc.  -->
 
|Designation      <!-- National Park, Nature Reserve, etc.  -->
Line 42: Line 45:
 
|Inland Rocky Areas, Subtropical/Tropical Dry Lowland Grassland, Subtropical/Tropical Dry Forest
 
|Inland Rocky Areas, Subtropical/Tropical Dry Lowland Grassland, Subtropical/Tropical Dry Forest
 
|}
 
|}
[http://www.unitar.org/hiroshima/sites/unitar.org.hiroshima/files/Annex%201%20-%20IUCN%20Classification%20Schemes.pdf IUCN habitat categories]  [[Site designations]]
+
[https://www.iucnredlist.org/resources/habitat-classification-scheme IUCN habitat categories]  [[Site designations]]
<br>
 
  
 
= Ape status =  <!-- a text overview of ape status (population sizes, trends etc), followed by a table of specific surveys and results -->
 
= Ape status =  <!-- a text overview of ape status (population sizes, trends etc), followed by a table of specific surveys and results -->
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In the 1970’s and 80’s, surveys conducted from vehicles or on foot confirmed chimpanzee presence in this area and estimated chimpanzee density at 0.08 chimpanzees per km2, resulting in a population of several hundred chimpanzees for the site (Sayer 1977, Moore 1985). More recent surveys by Pavy (1993) and Granier and Martinez (2004) estimated chimpanzee density at 0.27 and 0.35-0.4, respectively, yielding a population closer to, or above 1,000 individuals.
 
In the 1970’s and 80’s, surveys conducted from vehicles or on foot confirmed chimpanzee presence in this area and estimated chimpanzee density at 0.08 chimpanzees per km2, resulting in a population of several hundred chimpanzees for the site (Sayer 1977, Moore 1985). More recent surveys by Pavy (1993) and Granier and Martinez (2004) estimated chimpanzee density at 0.27 and 0.35-0.4, respectively, yielding a population closer to, or above 1,000 individuals.
  
 
+
'''Table 2. Great ape population estimates in Bafing'''
'''Table 2: Great ape population estimates in Bafing'''
 
 
{| border="1" cellpadding="5" cellspacing="0" class="population-estimate-table"
 
{| border="1" cellpadding="5" cellspacing="0" class="population-estimate-table"
 
! Species
 
! Species
 
! Year
 
! Year
! Abundance estimate (95% confidence interval)
+
! Abundance estimate (95% CI)
! Density estimate (per km²)
+
! Density estimate [ind./ km²] (95% CI)
 
! Encounter rate (nests/km)
 
! Encounter rate (nests/km)
 
! Area
 
! Area
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|Index survey
 
|Index survey
 
|Sayer 1977
 
|Sayer 1977
|‘Reconnaissance walk’
+
|Reconnaissance walk
 
|
 
|
 
|-
 
|-
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|
 
|
 
|South-west Mali; study area size: 5,000 km²
 
|South-west Mali; study area size: 5,000 km²
|Strip sampling (by road and by foot)
+
|Index survey
 
|Moore 1985
 
|Moore 1985
 
|Survey effort road: 650 km; survey effort foot: 100 km; extrapolation based on similar habitat types
 
|Survey effort road: 650 km; survey effort foot: 100 km; extrapolation based on similar habitat types
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no information on demographic trends to prove this (Kormos et al. 2003). The main causes of this population decline are hunting and agricultural expansion (Kormos et al. 2003), but road construction, human settlement, mining, and natural system modification causing flooding (Moor 1985, Kormos et al. 2003) are additional threats to chimpanzees and other wildlife species in this area.
 
no information on demographic trends to prove this (Kormos et al. 2003). The main causes of this population decline are hunting and agricultural expansion (Kormos et al. 2003), but road construction, human settlement, mining, and natural system modification causing flooding (Moor 1985, Kormos et al. 2003) are additional threats to chimpanzees and other wildlife species in this area.
  
 
+
'''Table 3. Threats to great apes in Bafing'''
'''Table 3: Threats to great apes in Bafing'''
 
 
{| border="1" cellpadding="5" cellspacing="0" class="threats-table"
 
{| border="1" cellpadding="5" cellspacing="0" class="threats-table"
 
!align="left"|Category  <!-- Do not change threat categories -->
 
!align="left"|Category  <!-- Do not change threat categories -->
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|-
 
|-
 
|1. Residential & commercial development
 
|1. Residential & commercial development
|1.1 Housing & Urban Areas
+
|1.1 Housing & urban areas
 
|Medium
 
|Medium
 
|
 
|
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|-
 
|-
 
|2. Agriculture & aquaculture
 
|2. Agriculture & aquaculture
|2.3 Livestock Farming & Ranching
+
|2.3 Livestock farming & ranching
 
|High
 
|High
 
|
 
|
 
|Settlement and agriculture are allowed inside the parks and reserves in Mali (Sayer 1977)
 
|Settlement and agriculture are allowed inside the parks and reserves in Mali (Sayer 1977)
|1977-2000 (2000: establishment of Bafing NP)
+
|1977-2000
 
|-
 
|-
 
|3. Energy production & mining
 
|3. Energy production & mining
|3.2 Mining & Quarrying
+
|3.2 Mining & quarrying
 
|Medium
 
|Medium
 
|
 
|
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|-
 
|-
 
|4. Transportation & service corridors
 
|4. Transportation & service corridors
|4.1 Roads & Railroads
+
|4.1 Roads & railroads
 
|Medium
 
|Medium
 
|
 
|
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|-
 
|-
 
|7. Natural system modifications
 
|7. Natural system modifications
|7.2 Dams & Water Management/Use
+
|7.2 Dams & water management/use
 
|High
 
|High
 
|
 
|
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|-
 
|-
 
|9. Pollution
 
|9. Pollution
|9.3 Agricultural & Forestry Effluents
+
|9.3 Agricultural & forestry effluents
 
|Low
 
|Low
 
|
 
|
|Area to be freed from onchocerciasis and trypanosomiasis; programmes to eliminate the vectors of the diseases are scheduled to take 20 years to complete (Sayer 1977)
+
|Area to be freed from onchocerciasis and trypanosomiasis; programmes to eliminate the vectors of the diseases are scheduled to take 20 years to complete (Sayer 1977).
 
|1977-1997
 
|1977-1997
 
|-
 
|-
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= Conservation activities =      <!-- a text overview of conservation activities, followed by a table of key activities -->
 
= Conservation activities =      <!-- a text overview of conservation activities, followed by a table of key activities -->
 
No conservation interventions have been reported for Bafing.
 
  
  
'''Table 4: Conservation activities in Bafing'''
+
'''Table 4. Conservation activities in Bafing'''
 
{| border="1" cellpadding="5" cellspacing="0" class="conservation-actions-table"
 
{| border="1" cellpadding="5" cellspacing="0" class="conservation-actions-table"
 
!align="left"|Category  <!-- Do not change threat categories -->
 
!align="left"|Category  <!-- Do not change threat categories -->
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[[Conservation activities list (Junker et al. 2017)]]
 
[[Conservation activities list (Junker et al. 2017)]]
  
= Impediments = <!-- Overview of impediments to ape conservation -->
+
= Challenges = <!-- Overview of impediments to ape conservation -->
  
No information on impediments has been documented.
 
  
 
+
'''Table 5. Challenges reported for Bafing'''
'''Table 5: Impediments reported for Bafing'''
 
 
{| border="1" cellpadding="5" cellspacing="0" class="impediments-table"
 
{| border="1" cellpadding="5" cellspacing="0" class="impediments-table"
!align="left"|Impediment  <!-- Do not change categories -->
+
!align="left"|Challenge <!-- Do not change categories -->
 
!Source  <!-- source for impediment mentioned -->
 
!Source  <!-- source for impediment mentioned -->
 
|-
 
|-
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= Research activities = <!-- Overview of research activities -->
 
= Research activities = <!-- Overview of research activities -->
  
No information on research activities has been documented.
 
  
 +
===Documented behaviors===  <!-- List of any behaviours observed at the site, including citations -->
  
===Documented behaviours===  <!-- List of any behaviours observed at the site, including citations -->
+
'''Table 6. Great ape behaviors reported for Bafing'''
 
 
 
 
'''Table 6: Great ape behaviors reported for Bafing'''
 
 
{| border="1" cellpadding="5" cellspacing="0" class="behaviors-table"
 
{| border="1" cellpadding="5" cellspacing="0" class="behaviors-table"
 
!align="left"|Behavior  <!-- Do not change categories -->
 
!align="left"|Behavior  <!-- Do not change categories -->
Line 338: Line 331:
 
|}
 
|}
  
 +
= 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 2°C. RCP 6.0 is a scenario with medium emissions in which global temperatures would likely rise up to 3°C 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).
  
===Relevant datasets===
+
'''Table 7. Estimated past and projected climatological characteristics in Bafing'''
[http://apesportal.eva.mpg.de/database/archiveMap A.P.E.S Portal]
+
{| border='1' cellpadding='5' cellspacing='0' class='EE-table'
 +
|
 +
|'''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]
 +
|28
 +
|29.2
 +
|29.1
 +
|29.5
 +
|30.9
 +
|-
 +
|Annual precipitation [mm]
 +
|1083
 +
|1099
 +
|1058
 +
|1045
 +
|985
 +
|-
 +
|Max no. consecutive dry days (per year)
 +
|112.4
 +
|111.1
 +
|119
 +
|116.1
 +
|119.7
 +
|-
 +
|No. days with heavy precipitation (per year)
 +
|2.6
 +
|4
 +
|4
 +
|3.9
 +
|3
 +
|-
 +
|}
 +
 
 +
 
 +
'''Table 8. Projected exposure of apes to extreme climate impact events in Bafing'''
 +
{| border='1' cellpadding='5' cellspacing='0' class='EE-table'
 +
|
 +
|'''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
 +
|6
 +
|0.01
 +
|2
 +
|0.01
 +
|4.5
 +
|0.01
 +
|11
 +
|0.01
 +
|-
 +
|Drought
 +
|1
 +
|50
 +
|1
 +
|75
 +
|0.25
 +
|25
 +
|2.25
 +
|100
 +
|-
 +
|Heatwave
 +
|0.5
 +
|50
 +
|0
 +
|0
 +
|0
 +
|0
 +
|0.5
 +
|50
 +
|-
 +
|River flood
 +
|0
 +
|0
 +
|0
 +
|0
 +
|0
 +
|0
 +
|0.25
 +
|0.02
 +
|-
 +
|Tropical cyclone
 +
|0
 +
|0
 +
|0
 +
|0
 +
|0
 +
|0
 +
|0
 +
|0
 +
|-
 +
|Wildfire
 +
|30
 +
|1.09
 +
|30
 +
|1.06
 +
|29
 +
|0.97
 +
|29
 +
|1.28
 +
|-
 +
|}
  
<br>
+
<div><ul>
 +
<li style="display: inline-block; vertical-align: top;"> [[File: PrecipAnomaly_Bafing.png | 450px | thumb| right | Precipitation anomaly in Bafing]] </li>
 +
<li style="display: inline-block; vertical-align: top;"> [[File: TempAnomaly_Bafing.png | 450px | thumb| right | Temperature anomaly in Bafing]] </li>
 +
</ul></div>
  
 
= References =
 
= References =
 
Duvall C S. 2008. Human settlement ecology and chimpanzee habitat selection in Mali. Landscape Ecology 23: 699-716.<br>
 
Duvall C S. 2008. Human settlement ecology and chimpanzee habitat selection in Mali. Landscape Ecology 23: 699-716.<br>
 
Granier N., Martinez L. 2004. Première reconnaissance des chimpanzés ''Pan troglodytes verus'' dans la zone transfontalière entre la Gunée et le Mali (Afrique de l’Ouest). Primatologie 6: 423-447.<br>
 
Granier N., Martinez L. 2004. Première reconnaissance des chimpanzés ''Pan troglodytes verus'' dans la zone transfontalière entre la Gunée et le Mali (Afrique de l’Ouest). Primatologie 6: 423-447.<br>
 +
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.<br>
 
Kormos R, Boesch C, Bakarr M I, Butynski T. (eds.). 2003. West African Chimpanzees. Status Survey and Conservation Action Plan. IUCN/SSC Primate Specialist Group. IUCN, Switzerland and UK.<br>
 
Kormos R, Boesch C, Bakarr M I, Butynski T. (eds.). 2003. West African Chimpanzees. Status Survey and Conservation Action Plan. IUCN/SSC Primate Specialist Group. IUCN, Switzerland and UK.<br>
 
Kortlandt A 1983. Marginal habitats of chimpanzees. Journal of Human Evolution: 12 231–278.<br>
 
Kortlandt A 1983. Marginal habitats of chimpanzees. Journal of Human Evolution: 12 231–278.<br>

Latest revision as of 09:42, 9 October 2024

West Africa > Mali > Bafing

Summary

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  • Western chimpanzees (Pan troglodytes verus) are present in Bafing.
  • It has been estimated that between 417-1,408 individuals occurred in the site in 1993.
  • The chimpanzee population trend is unknown.
  • This site has a total size of 5000 km².
  • Key threats to chimpanzees is habitat degradation due to subsistence farming.
  • No conservation activities were reported for Bafing.
  • Hottest and driest place in which western chimpanzees exist. Chimpanzees do not seem to be restricted to riverine forest, but are spread widely through woodland.

Site characteristics

Bafing (Mali) © E.Terrade

Bafing is situated in southern Mali. The current status of the site is not known. This site is 5000 km² (World Database on Protected Areas 2019). Woodlands dominate most of the landscape. During his survey of south-western Mali, Moore (1985) regularly observed buffalo Syncerus caffer, roan Hippotragus equinus, hartebeest Alcelaphus buselaphus, and warthog Phacochoerus africanus. Sayer (1977) encountered giant eland Tragelaphus derbianus and giraffe Giraffa camelopardalis in this area. Lion Panthera leo, leopard Panthera pardus, and African wild dog Lycaon pictus also probably occur at very low densities (Moore 1985). The current state of biodiversity is not known. Although this is the hottest and driest place in which western chimpanzees are known to exist (Kortlandt 1983), chimpanzees at this site do not seem to be restricted to riverine forest, but are spread widely through the woodland (Moore 1985).

Table 1. Basic site information for Bafing

Area 5000 km²
Coordinates 12.90, -10.58
Designation Unknown
Habitat types Inland Rocky Areas, Subtropical/Tropical Dry Lowland Grassland, Subtropical/Tropical Dry Forest

IUCN habitat categories Site designations

Ape status

In the 1970’s and 80’s, surveys conducted from vehicles or on foot confirmed chimpanzee presence in this area and estimated chimpanzee density at 0.08 chimpanzees per km2, resulting in a population of several hundred chimpanzees for the site (Sayer 1977, Moore 1985). More recent surveys by Pavy (1993) and Granier and Martinez (2004) estimated chimpanzee density at 0.27 and 0.35-0.4, respectively, yielding a population closer to, or above 1,000 individuals.

Table 2. Great ape population estimates in Bafing

Species Year Abundance estimate (95% CI) Density estimate [ind./ km²] (95% CI) Encounter rate (nests/km) Area Method Source Comments A.P.E.S. database ID
Pan troglodytes verus 1972-1974 Present Parc National du Baoulé and its three adjacent reserves of Fina, Badinnko and Kongossombougou, and the surrounding controlled hunting areas; study area size: 10,000 km² Index survey Sayer 1977 Reconnaissance walk
Pan troglodytes verus 1984 700 0.08 South-west Mali; study area size: 5,000 km² Index survey Moore 1985 Survey effort road: 650 km; survey effort foot: 100 km; extrapolation based on similar habitat types
Pan troglodytes verus 1993 1,408 0.27 Bafing; study area size: 5,200 km² Informed guess Pavy 1993, in Kormos et al. 2003 Results of a “nest survey” were extrapolated to probable chimpanzee habitat
Pan troglodytes verus 2003- 2004 0.35-0.4 6.5 Area near camps Fari, Faragama, Djakoli Line transect (Distance) Granier & Martinez 2004 Survey effort: 29 km on 18 line transects; 190 nests observed
Pan troglodytes verus 2004 Present Area around Solo village in Bafing; study area size: 183 km² Index survey Duvall 2008 Duvall (2008) walked loops of 62 km twice weekly for several months, encountered chimpanzee groups directly (48) or indirectly (224) on 272 occasions (Duvall 2008)

Threats

Populations of several other species of large wild animals in Mali have declined drastically (Sayer 1977, Moore 1985), and it therefore seems probable that Mali’s chimpanzee population has also declined, although there is no information on demographic trends to prove this (Kormos et al. 2003). The main causes of this population decline are hunting and agricultural expansion (Kormos et al. 2003), but road construction, human settlement, mining, and natural system modification causing flooding (Moor 1985, Kormos et al. 2003) are additional threats to chimpanzees and other wildlife species in this area.

Table 3. Threats to great apes in Bafing

Category Specific threats Threat level Quantified severity Description Year of threat
1. Residential & commercial development 1.1 Housing & urban areas Medium Settlement and agriculture are allowed inside the parks and reserves in Mali (Sayer 1977, Duvall 2008) Ongoing (2008)
2. Agriculture & aquaculture 2.3 Livestock farming & ranching High Settlement and agriculture are allowed inside the parks and reserves in Mali (Sayer 1977) 1977-2000
3. Energy production & mining 3.2 Mining & quarrying Medium Gold-mining near Kéniéba and Sadiola (Caspary et al. 1998, in Kormos et al. 2003) Ongoing (2003)
4. Transportation & service corridors 4.1 Roads & railroads Medium Proposed road connecting Bamako and Dakar passing through Kouroukoto (Kormos et al. 2003) Ongoing (2003)
5. Biological resource use 5.1 Hunting & collecting terrestrial animals Present The killing of chimpanzees to protect crops and wild fruit trees has been reported for parts of Mali (Duvall 2008, Moore 1985, Sayer 1977), in other areas there are taboos against hunting chimpanzees (Terrade pers. obs.) Ongoing (2008)
6. Human intrusions & disturbance Unknown
7. Natural system modifications 7.2 Dams & water management/use High A large dam constructed on Bafing river at Manantali flooding some 500 km2 (Moore 1985) 1990
8. Invasive & other problematic species, genes, diseases Unknown
9. Pollution 9.3 Agricultural & forestry effluents Low Area to be freed from onchocerciasis and trypanosomiasis; programmes to eliminate the vectors of the diseases are scheduled to take 20 years to complete (Sayer 1977). 1977-1997
10. Geological Events Absent
11. Climate change & severe weather Unknown
12. Other options Absent

IUCN Threats list

Conservation activities

Table 4. Conservation activities in Bafing

Category Specific activity Description Year of activity
1. Residential & commercial development Not reported
2. Agriculture & aquaculture Not reported
3. Energy production & mining Not reported
4. Transportation & service corridors Not reported
5. Biological resource use Not reported
6. Human intrusions & disturbance Not reported
7. Natural system modifications Not reported
8. Invasive & other problematic species, genes, diseases Not reported
9. Pollution Not reported
10. Education & Awareness Not reported
11. Habitat Protection Not reported
12. Species Management Not reported
13. Livelihood; Economic & Other Incentives Not reported

Conservation activities list (Junker et al. 2017)

Challenges

Table 5. Challenges reported for Bafing

Challenge Source
Not reported

Research activities

Documented behaviors

Table 6. Great ape behaviors reported for Bafing

Behavior Source
Honey eating Kühl et al. 2019
Termite fishing Kühl et al. 2019
Termite eating Kühl et al. 2019

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 2°C. RCP 6.0 is a scenario with medium emissions in which global temperatures would likely rise up to 3°C 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 7. Estimated past and projected climatological characteristics in Bafing

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] 28 29.2 29.1 29.5 30.9
Annual precipitation [mm] 1083 1099 1058 1045 985
Max no. consecutive dry days (per year) 112.4 111.1 119 116.1 119.7
No. days with heavy precipitation (per year) 2.6 4 4 3.9 3


Table 8. Projected exposure of apes to extreme climate impact events in Bafing

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 6 0.01 2 0.01 4.5 0.01 11 0.01
Drought 1 50 1 75 0.25 25 2.25 100
Heatwave 0.5 50 0 0 0 0 0.5 50
River flood 0 0 0 0 0 0 0.25 0.02
Tropical cyclone 0 0 0 0 0 0 0 0
Wildfire 30 1.09 30 1.06 29 0.97 29 1.28
  • Precipitation anomaly in Bafing
  • Temperature anomaly in Bafing

References

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Granier N., Martinez L. 2004. Première reconnaissance des chimpanzés Pan troglodytes verus dans la zone transfontalière entre la Gunée et le Mali (Afrique de l’Ouest). Primatologie 6: 423-447.
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.
Kormos R, Boesch C, Bakarr M I, Butynski T. (eds.). 2003. West African Chimpanzees. Status Survey and Conservation Action Plan. IUCN/SSC Primate Specialist Group. IUCN, Switzerland and UK.
Kortlandt A 1983. Marginal habitats of chimpanzees. Journal of Human Evolution: 12 231–278.
Kühl H S, Boesch C, Kulik L, Hass F, Arandjelovic M, Dieguez P, et al. 2019. Human impact erodes chimpanzee behavioral diversity. Science 363: 1453–1455.
Moore J J. 1985. Chimpanzee survey in Mali, West Africa. Primate Conservation 6: 59–63.
Sayer J A. 1977. Conservation of large mammals in the Republic of Mali. Biological Conservation 12: 245–263.



Page completed by: A.P.E.S. Wiki Team & E. Terrade Date: 18/11/2019