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Mpumalanga Biodiversity Conservation Plan Handbook - bgis-sanbi

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MPUMALANGA BIODIVERSITY CONSERVATION PLAN HANDBOOK<br />

22<br />

Dung Beetle<br />

possibly Anachalcos convexus<br />

Insects like dung beetles<br />

have an important role to<br />

play as decomposers and<br />

waste removal specialists.<br />

There are several families<br />

and thousands of species<br />

of dung beetle. By<br />

burying and eating dung,<br />

the beetles help nutrient<br />

cycling and improve soil<br />

structure. Dung beetles<br />

reportedly save the<br />

United States cattle<br />

industry an estimated<br />

$380 million annually by<br />

burying above-ground<br />

livestock faeces.<br />

WHAT IS SYSTEMATIC BIODIVERSITY PLANNING?<br />

The process of identifying spatial biodiversity priorities in the MBCP is based on the<br />

Systematic <strong>Biodiversity</strong> <strong>Plan</strong>ning approach of Margules and Pressey (2000), also referred to as<br />

Systematic <strong>Conservation</strong> <strong>Plan</strong>ning. The underlying principle is to identify representative<br />

samples of biodiversity that are located where they can persist over the long term. The<br />

amount of biodiversity requiring protection must then be quantified by setting a target for<br />

each biodiversity feature. This numerical target tells us how much of the feature needs to be<br />

maintained or conserved, in order for it to persist and contribute to ecosystem functioning.<br />

BOX 4.1: STEPS IN SYSTEMATIC BIODIVERSITY PLANNING<br />

(Margules & Pressey 2000)<br />

Systematic <strong>Biodiversity</strong> <strong>Plan</strong>ning has a set (systematic) sequence of procedures<br />

1. Select and collate the biodiversity features and surrogates to be used in the<br />

planning area.<br />

2. Formulate explicit conservation goals that can be expressed as quantifiable<br />

biodiversity targets.<br />

3. Review the extent to which goals have been met in existing reserves.<br />

4. Use systematic methods to locate and design feasible new reserves that are<br />

able to protect the remainder of the biodiversity targets (that are not currently<br />

protected).<br />

5. Prioritise and implement conservation actions on the ground.<br />

6. Manage and monitor (adaptive management) within reserves to maintain<br />

biodiversity features.<br />

Systematic biodiversity planning is at a more advanced stage for terrestrial than for aquatic<br />

ecosystems, usually resulting in such plans being done separately. The MBCP is the first<br />

provincial biodiversity plan to successfully integrate the two. Systematic biodiversity planning<br />

makes use of sophisticated planning software to calculate the most efficient pattern of<br />

planning units required to meet biodiversity targets. The MBCP used a software package<br />

called Marxan (Possingham et al. 2000) briefly explained in the box below.<br />

BOX 4.2: BIODIVERSITY PLANNING SOFTWARE USED IN<br />

MBCP –– MARXAN AND CLUZ<br />

Cluz is a user-friendly ArcView GIS interface that allows users to design protected<br />

area networks based on the Marxan algorithm. Its efficiency lies in linking the Marxan<br />

conservation planning software with ArcView and in importing of data, analysis and<br />

exporting of output data.<br />

Marxan is designed to produce very efficient solutions to the problem of selecting planning<br />

units that meet a suite of biodiversity targets. Although several other conservation planning<br />

packages are available (such as C-plan), Marxan is unique in that it is able to address three<br />

important functions. These are:<br />

Incorporating boundary cost;<br />

Incorporating planning unit cost;<br />

Setting clump targets.<br />

Marxan then aims to minimise the cost of the above three functions by adding a cost value<br />

to them, and then trying to minimise planning unit portfolio costs.<br />

continued overleaf

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