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Ecosystem Guidelines for Environmental Assessment

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SCEPS<br />

4<br />

Which spatial components of ecological processes have been mapped<br />

For reasons of scale and prioritisation of regional conservation actions, not all spatial components of<br />

ecological processes are mapped in biodiversity plans.<br />

In general, only those large-scale ecological processes deemed to be important <strong>for</strong> achieving biodiversity<br />

targets at the broad, biome level have been mapped; numerous ecological corridors or vegetation<br />

boundaries that represent more localised but equally important processes at the scale of landscapes<br />

and catchments have not been mapped in most biodiversity plans.<br />

Spatial components of ecological processes have been mapped as follows:<br />

The C.A.P.E. plan mapped selected fixed processes, e.g. edaphic interfaces, sand movement corridors<br />

and riverine corridors. Flexible processes, such as upland-lowland gradients and macro-climatic<br />

gradients, were mapped by finding the most efficient routes or paths <strong>for</strong> these gradients through intact<br />

natural habitat.<br />

The STEP Conservation Priority Map captures fixed processes as "Process areas" and flexible processes<br />

as "Conservation paths" that provide the core areas <strong>for</strong> the proposed Mega-conservancy Network.<br />

The SKEP project mapped a separate layer of fixed processes, which includes quartz and gravel<br />

patches, sand movement corridors, and soil interfaces. Flexible processes are shown as arrows<br />

representing upland-lowland gradients and climatic gradients.<br />

The Cape Lowlands Renosterveld Plan mapped a number of ecological processes at 1:50 000 scale,<br />

namely soil type transitions, river corridors, upland-lowland gradients, upland-lowland transitions<br />

(interfaces) and coast-interior gradients.<br />

5<br />

Table 4 (see overleaf) summarises the fixed<br />

processes recognised by the CAPE and STEP<br />

projects and provides some examples of their<br />

location. The majority of spatial components of<br />

ecological processes can be mapped either as an<br />

ecological corridor, or as a boundary between two<br />

ecosystems or vegetation types. We suggest that<br />

<strong>for</strong> the purposes of environmental assessment, it<br />

may be more useful to think in terms of "ecological<br />

corridors and vegetation boundaries" rather than<br />

"spatial components of ecological processes",<br />

which can be difficult to conceptualise.<br />

Spatial components of ecological processes are surrogates<br />

<strong>for</strong> depicting ecological processes such as pollination.<br />

The conservation of important ecological corridors and vegetation boundaries<br />

At landscape level, environmental assessment practitioners, biodiversity specialists and spatial planners<br />

need to:<br />

BOTANICAL SOCIETY OF SOUTH AFRICA<br />

Refer to existing systematic biodiversity plans in order to determine which important fixed or flexible<br />

ecological processes have been identified and mapped in the affected area. Where these areas have<br />

been mapped, it is essential to ensure that sufficient habitat is set aside and/or managed to support<br />

those ecological processes <strong>for</strong> which each spatial component was identified.<br />

SPATIAL COMPONENTS OF ECOLOGICAL PROCESSES : 83

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