African Wild Dog Conservancy

Land area
  • 3,824 km2

With an area of over 3,800 km2, African Wild Dog conservancy covers a large area in the south of the landscape. The conservancy was gazetted in 2005 and over 4,400 people live here. Annual rainfall is 350 - 400 mm.

With an area of over 3,800 km2, African Wild Dog conservancy covers a large area in the south of the landscape. The conservancy was gazetted in 2005 and over 4,400 people live here. Annual rainfall is 350 - 400 mm.

Literature for African Wild Dog Conservancy


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  • Information on African Wild Dog Conservancy

    Information on African Wild Dog Conservancy from NACSO website

    Fact sheets, notice-board posters etc on African Wild Dog Conservancy
  • Vegetation of the eastern communal conservancies in Namibia. Part 1

    Strohbach BJ 2014. Vegetation of the eastern communal conservancies in Namibia: I. Phytosociological descriptions, Koedoe 56(1), Art. #1116, 18 pages

    The establishment of communal conservancies aims to have the local communities share in the benefits especially of wildlife resources, in this way spearheading the conservation of the environment. The Desert Margins Programme in Namibia aimed to develop vegetation resource data for the Otjituuo, Okamatapati, Ozonahi, African Wild Dog, Otjinene, Epukiro, Otjombinde, Omuramba Ua Mbinda, Eiseb and Ondjou communal conservancies, in order to assist with natural resource planning. For this purpose, a phytosociological survey of this area, with 422 relevés, was conducted during 2004. Thirteen vegetation associations were formally described in this article, of which two were subdivided into subassociations. These associations can broadly be grouped into broad-leaved savanna types typical of the central and northern Kalahari of Namibia and microphyll savannas found on the transitions to the Central Plateau. Threats to the vegetation include overutilisation and regular fires, both of which could easily lead to desertification. This threat is aggravated by global climate change.
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  • Vegetation of the eastern communal conservancies in Namibia. Part 2

    Strohbach BJ 2014. Vegetation of the eastern communal conservancies in Namibia: II. Environmental drivers, Koedoe 56(1), Art. #1117, 12 pages

    The eastern communal conservancies are situated along the western fringe of the Kalahari basin. Under a very short rainfall gradient, the vegetation abruptly changes from microphyllous Acacia-dominated savannas to mesophyll savannas, dominated by Terminalia sericea and Combretum spp. We hypothesise that this is caused by changes in soil moisture availability brought about by changes in soil texture from loamy soils to deep sands (the ‘inverse texture effect’). For this analysis, we used vegetation and soils data derived from a recognisance survey of the natural resources of the study area. As the sites in the soil and vegetation surveys did not overlap, it was decided to use only synoptic data for the plant associations in the analysis. Non-metric multidimesional scaling ordination was utilised as ordination technique of the vegetation data and various environmental parameters, including soil texture, soil hydraulic parameters, climatic and fire regime parameters, were overlaid as biplots onto the resulting graph, as were various plant functional attributes particularly related to climatic conditions. The main environmental gradient identified within the study area is the rainfall gradient. This relatively short gradient, however, does not explain the marked change in vegetation observed within the study area. This change is attributed to the change in soil type, in particular, the soil texture and the associated soil hydraulic parameters of the soil. This gradient is closely correlated to leaf size, explaining the change from microphyll savannas to mesophyll savannas along the change from loamy to sandy soils. One of the lesser understood mechanisms for the survival of these mesophyll plants on sandy soils seems to be a deep root system, which is actively involved in water redistribution within the soil profile – by hydraulic lift, inverse hydraulic lift and stem flow.
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