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Artiodactyla Id code: amd159

Bovidae

Connochaetes taurinus

(Burchell, 1823)

(Eng) Brindled gnu or blue wildebeest

(Fre) Gnou à queue noire

Taxonomic notes

Five subspecies have been described (East, 1996).

IUCN threat category

Lower Risk, conservation dependent (LR: cd) as C. t. albojubatus (Eastern white-beared wildebeest) in Kenya, Tanzania; as C. t. cooksoni (Cookson’s wildebeest) in Malawi, Zambia; as C. t. johnstoni (Niassa wildebeest) in Malawi (ex), Mozambique, Tanzania; as C. t. mearnsi (Western white-beared wildebeest) in Kenya, Tanzania; and as C. t. taurinus (Blue wildebeest) in Angola, Botswana, Mozambique, Namibia, South Africa, Swaziland, Zambia, Zimbabwe.

Available information

The ecology of the blue wildebeest has been widely studied in most of its range of distribution.

East Africa: Particular aspects of habitat use are analysed in two papers. A study on the effects of seasonal changes in water availability on several large mammals species, including the blue wildebeest, was conducted in Amboseli by Western (1975). In Lake Burungi (Tanzania), Moe et al. (1990) analysed the use of burnt areas by large herbivores and the effects on their distribution. In the Serengeti system, the migratory behaviour of the species was studied by several authors (McNaughton, 1976; Northon-Griffiths, 1973; Pennycuick, 1975). Information on the feeding habits is found in Murray (1993) and Stewart & Stewart (1971). A study of the role of food availability on the population mortality rate was also conducted in the area by Sinclair et al. (1985).

Southern Africa: Habitat requirements and selection were analysed by Hirst (1975) and Ben-Shahar (1995), who both studied the species in the Transvaal lowveld; Ben Shahar (1991) also gives detailed information on its feeding ecology. Data on activity patterns are available from Berry et al. (1982) and Ben-Shahar & Fairall (1987). Studies on population structure and dynamics were carried out by Attwell (1982) in Kwa-Zulu Natal, and by Whyte & Joubert (1988) in the Transvaal lowveld, where its migratory behaviour was also investigated (Thrash et al., 1995; Eloff, 1966). Seasonal distribution in the Makgadikgadi Pans (Botswana) is described in Kgathi & Kalikawe (1993). Status and distribution has recently been accurately monitored in Botswana (Anonymous, 1993, 1994a, 1994b, 1995; Spinage, 1992). Data on distribution, status, and ecology are also available for some areas of South Africa (Lynch, 1983, 1989; Rowe-Rowe, 1994). A very detailed account of the ecology of the species in the subregion is found in Mills & Hes (1997) and Skinner & Smithers (1990), while general information on the species' ecology is given in Estes (1991) and Kingdon (1997). Status and distribution, together with some ecological notes, are discussed in East (1988, 1989).

Known extent of occurrence

Extinct in Malawi, this gnu still ranges in Angola, Botswana, Kenya, Mozambique, Namibia, South Africa, Swaziland, Tanzania, Zambia, Zimbabwe (East, 1996; Wilson & Reeder, 1993) with its southernmost limit along the Orange River (Estes, 1991). Its distribution map was obtained from Estes (1991), then refined using detailed country maps in East (1988, 1989) as indicated by Dr. R. East (23 June '97) (Fig. 8.6.4.a).

Categorical-discrete (CD) distribution model

Found mainly in short-grass savanna; the species is also found in open woodland and bushland. Water bound (Lynch, 1983; East, 1988, 1989; Hirst, 1975; Kingdon, 1997; Van der Walt, 1986; Ben-Shahar, 1995; Stuart & Stuart, 1997; Mills & Hes, 1997).

Based on these environmental preferences, the following scores were assigned (Fig. 8.6.4.b) (8.6.4.a):

Score

 

1(*)

Grasslands and grassland mosaics.

2

Open woodlands; open bushlands.

3

Altimontane vegetation; croplands; forests and forest mosaics; dense bushlands and thickets.

(*) Scores decreased for vegetation types occurring outside a 10-km buffer around permanent water.

 

suitable

moderately suitable

unsuitable

Total

km2

%

km2

%

km2

%

km2

%

1 183 242

37

1 753 459

55

242 707

8

3 179 408

100

Tab 8.6.4.a: Cumulative size (km2) of areas pertaining to the different 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

683

1 705

19 978

15.74

1.46

15.97

moderately suitable

1 473

1 163

31 524

41.93

1.34

13.98

Total AO

124

23 214

208 285

80.22

1.48

11

Tab 8.6.4.b: Area of Occupancy fragmentation indexes.

Probabilistic-continuous (PC) distribution model

The output of the probabilistic-continuous (PC) distribution model is shown in Fig. 8.6.4.c.

Validation

% of EO in sample areas

Number of valid plots

Index of Accordance (%)

17.72

86

48.84

Tab 8.6.4.c: Categorical-discrete (CD) distribution model validation parameters.

Comments and conservation issues

The low Index of Accordance (48.84%) possibly reflects the limitations on the species distribution induced by the veterinary fences in Botswana, nevertheless it may suggest some caution in the interpretation of the results of the CD model. Most of the known EO is suitable for this species (92%) and this also reflects the possibility of drawing an accurate EO for large and visible mammals. The best areas are certainly very fragmented (NP and MPS) but the overall AO is not; the LPI of the total AO is quite high (80.22%) and the AWMSI shows that the patches are relatively compact. The most desert areas of Namibia and Botswana appear to be the least suitable according to the CD model. A significant portion of the AO is included in existing protected areas (almost 15%) and the average status of the species is classified as Lower Risk: local races may be more threatened.

SUITABILITY CLASS

inside

outside

Total

suitable

6.19

31.02

37.22

moderately suitable

7.87

47.28

55.15

unsuitable

0.95

6.69

7.63

Total

15.01

84.99

100

Tab 8.6.4.d: Percent of environmental suitability classes within EO (as derived from the categorical-discrete distribution model) inside and outside the protected areas.

References

Anonymous (1993). Aerial census of animals in northern Botswana. ULG Consultants LTD Birmingham Road, Satisford Warwick CV34 4TT England.

Anonymous (1994a). Aerial census of animals in Botswana: wet season 1994. Wildlife conservation in northern Botswana.

Anonymous (1994b). Status and trends of selected wildlife species in Botswana. Department of Wildlife and National Park: Research Division.

Anonymous (1995). The status of wildlife in Botswana. Serondella News. Official newsletter of Chobe Wildlife Trust.: 6 (5), 1-12.

Attwell C.A.M. (1982). Population ecology of the blue wildebeest Connochaetes taurinus taurinus in Zululand, South Africa. Afr. J. Ecol.: 20, 147-168.

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Ben-Shahar R. (1995). Habitat classification in relation to movements and densities of ungulates in a semi-arid savanna. Afr. J. Ecol.: 33 (1), 50-63.

Ben-Shahar R., Fairall N. (1987). Comparison of the diurnal activity patterns of blue wildebeest and red hartebeest. S. Afr. J. Wildl. Res.: 17(2), 49-54.

Berry H.H., Stegfried W.R., Crowe T.M. (1982). Activity pattern in a population of free-ranging wildebeest (Connochaetes taurinus) at Etosha National Park. Z. Tierpsychol.: 59, 229-246.

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