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Primates Id code: amd075

Cercopithecidae

Colobus polykomos

(Zimmermann, 1780 )

(Eng) Western black-and-white colobus

(Fre) Colobe blanc-et-noir d’Afrique occcidentale

Taxonomic notes

The number of taxonomically distinct populations that can be identified within the genus Colobus and their phylogenetic relationships are still under debate (Oates & Trocco, 1983). As suggested by Oates & Trocco (1983) and Oates (1996) C. vellerosus C. angolensis and C. satanas have been considered fully distinct species here, while Wilson & Reeder (1993) as well as other authors consider C. vellerosus as conspecific with C. polykomos.

IUCN threat category

Lower Risk, near threatened (LR: nt).

Available information

Taxonomy and phylogeny discussion of this species are discussed in Oates & Trocco (1983). Information on the species' ecology and distribution is found in Kingdon (1997) and Stuart & Stuart (1997), while eco-ethological notes are reported by Galat & Galat-Luong (1985). Status, threats, and conservation issues are discussed in Oates (1996).

Known extent of occurrence

According to the above classification, C. polykomos and C. vellerosus are allopatric species separated by the Bandama River, the former occurring to the west of it and ranging from Ivory Coast to Gambia and Senegal (Wilson & Reeder, 1993; Oates, 1996; Kingdon, 1997). A first rough distribution map was obtained from the overlay of the two maps published by Estes (1991) and Oates & Trocco (1983), but it was then revised and updated to match the river network and other reliable published distribution records (Oates, 1996; Kingdon, 1997). The map (Fig. 2.3.35.a) should not be considered to reflect this monkey's present range accurately; further information is required.

Categorical-discrete (CD) distribution model

This species occurs mostly in forests and gallery forests (Kingdon, 1997; Booth, 1979).

Based on these environmental preferences, the following scores were assigned (Fig. 2.3.35.b) (Tab. 2.3.35.a):

Score (*)

 

1

Forests.

2

Forest mosaics.

3

Savannas and croplands.

(*) Scores increased for vegetation types occurring inside a 1-km buffer around permanent water.

 

suitable

moderately suitable

unsuitable

Total

km2

%

km2

%

km2

%

km2

%

228 210

44

165 531

32

127 063

24

520 804

100

Tab 2.3.35.a: Cumulative size (km2) of areas pertaining to each environmental suitability class within the Extent of Occurrence.

Number Patches (NP)

Mean Patch Size (MPS) km2

Patch Size SD (PSSD) km2

Largest Patch Index (LPI) %

Mean Shape Index (MSI)

Area-Weighted Mean Shape Index (AWMSI)

suitable

238

955

12 033

46.83

1.34

19.99

moderately suitable

667

249

2 131

13.35

1.43

9.37

Total AO

153

2 571

30 156

95.18

1.48

10.86

Tab 2.3.35.b: Area of Occupancy fragmentation indexes.

Probabilistic-continuous (PC) distribution model

The output of the probabilistic-continuous (PC) distribution model is shown in Fig. 2.3.35.c.

Validation

No occurrence of the species within the four sample areas.

 

Comments and conservation issues

The known EO, rather abruptly cut at the Bandama River, extends into Senegal to include the Gambia River gallery forests. However, the largest patches of unsuitable areas appear to be mostly in the easternmost parts of the range and they should be verified for the species’ presence. Forest continuity throughout the range appears ensured by the contribution of different classes of forests and forest mosaics, and the overall fragmentation of the AO is thus limited. The LPI of the suitable areas is 46.83% indicating a significant continuous good patch, but the AWMSI also shows that the shape of these suitable areas is such that they are highly interspersed with other less suitable areas. Although the species is classified as Lower Risk, it is poorly protected by the existing protected areas which include less than 4% of the total AO.

SUITABILITY CLASS

inside

outside

Total

suitable

1.65

42.17

43.82

moderately suitable

1.48

30.30

31.78

unsuitable

1.76

22.64

24.40

Total

4.88

95.12

100

Tab 2.3.35.c: Percent of environmental suitability classes within EO (as obtained from the categorical-discrete distribution model) inside and outside the protected areas.

References

Booth A.H. (1979). The distribution of primates in the Gold Coast. In: Sussman R.W. (Ed.). Primate Ecology. Problem-oriented field studies. Wiley, Chichester & New York: chap. 7: 139-154.

Estes R.D. (1991). The Behavior Guide to African Mammals. Including Hoofed Mammals, Carnivores, Primates. The University of California Press.

Galat G., Galat-Luong A. (1985). La communauté de Primates diurnes de la foret de Tai, Côte d'Ivoire. Revue de Ecologie (La Terre et la Vie): 40, 7-32.

Kingdon J. (1997). The Kingdon field guide to African Mammals. Academic Press, London and New York: Natural World.

Oates J.F. (1996). African Primates Status Survey and Conservation Action plan. IUCN/SSC Primate Specialist Group.

Oates J.F., Trocco T.F. (1983). Taxonomy and phylogeny of black-and-white colobus monkeys: inferences from an analysis of loud call variation. Folia Primatol.: 40, 83-113.

Stuart C., Stuart T. (1997). Field guide to the larger mammals of Africa. Struik Publishers.

Wilson D.E., Reeder D.M. (Eds) (1993). Mammal Species of the World: A Taxonomic and Geographic Reference. Second edition. Smithsonian Institution Press, Washington D.C.