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Mpumalanga Biodiversity Conservation Plan Handbook - bgis-sanbi

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MPUMALANGA BIODIVERSITY CONSERVATION PLAN HANDBOOK<br />

42<br />

Roan<br />

Hippotragus equinus<br />

Antelope form the basis<br />

of a major tourism<br />

industry. Not only do<br />

tourists pay substantial<br />

sums to see antelope but<br />

they also visit to see the<br />

predators of antelope.<br />

Roan antelope are rare or<br />

endangered over most of<br />

their range because they<br />

have very specific habitat<br />

requirements<br />

DATA USE AND LIMITATIONS<br />

The data used to compile this plan and the scientific knowledge that underpins the<br />

biodiversity targets are currently the best available. The MBCP database has been collected<br />

over many years and from diverse sources. Although data and sources have been checked<br />

and verified, gaps and errors may exist. Satellite data, such as the land transformation<br />

coverage, are derived from images taken in 1995 and 2000. This means that six years of<br />

ongoing transformation is not recorded in the MBCP.<br />

All data and the information on the MBCP map, especially in contentious situations, should<br />

be verified on the ground, preferably by an ecologist with local experience, before a<br />

.<br />

decision about land-use is taken. Data from the verification process, especially corrections,<br />

must be captured and archived to update and add to the information on which future<br />

biodiversity planning will be based<br />

The MBCP has created six biodiversity conservation categories for terrestrial ecosystems using<br />

systematic biodiversity planning methods (Table 6.1). This chapter sets out broad land-use<br />

guidelines applicable to each category and all ecosystems.<br />

The MBCP has also identified the most important water catchments in the Province which are<br />

critical for meeting aquatic biodiversity targets (see Figure 4.2). Land-use guidelines for these<br />

catchments are provided to safeguard their current good ecosystem status. All land<br />

uses involving physical development will have significant impacts on these catchments. It is<br />

critical that inappropriate development does not compromise their integrity. Both aquatic<br />

biodiversity and water supplies will be jeopardised if this is allowed to happen.<br />

TERRESTRIAL ECOSYSTEMS<br />

TABLE 6.1: Summary of terrestrial biodiversity conservation categories<br />

BIODIVERSITY CONSERVATION CATEGORY % OF PROVINCE COMMENT ON<br />

LAND USE<br />

1. PAs currently under formal biodiversity protection PAs - 14.8%<br />

2. Irreplaceable, in urgent need of protection and PA status Irrp - 2.4%<br />

3. Highly Significant, protection needed - limited choice for H-S - 12.3%<br />

meeting targets<br />

4. Important and Necessary, protection needed - I&N - 9.5%<br />

more choices for meeting targets<br />

5. Areas of Least Concern, providing options for development L-C - 25.2%<br />

6. Areas with No Natural Habitat remaining, providing NN - 35.8%<br />

preferred sites for all forms of development.<br />

(Ecological corridors (6.7%) are not included as they are not part of the spatial analysis.)<br />

The higher conservation<br />

categories (1 to 4)<br />

need to be managed<br />

for the conservation of<br />

biodiversity.<br />

61% of Province<br />

available for development<br />

via EIA planning<br />

procedures.

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