Targeting Tsetse Control

GIS (Geographical Information System) data can be easily used to help identify areas where disease control measures are best carried out. A current example is that of defining the best areas for feasibility studies for tsetse control in West Africa.

 

In this study, the broad areas where impact is likely to be high were identified from the predicted impact map as defined by PAAT-IS (the darker parts in the blue rectangle), and where control measures have not already been used (the grey parts). 

 

 

 

As a next step, farming intensity was estimated by overlaying data on cattle densities and percentage of land under the cultivation cycle. This enables us to highlight areas that may produce maximum economic benefit – i.e. in the tsetse belt but near centres of agriculture (shown in dark green and red) from which farmers will spread into any newly cleared areas.

 

Next the technical feasibility of tsetse control has to be considered. Areas have to be identified where both tsetse is (relatively) easy to clear, and there is minimal risk of the new farming causing environmental degradation. In the picture on the left, degradation is shown in vivid red, high population density in dark blue, protected areas in dark green, and previously controlled areas in grey. Fly presence is in yellow and bright green. 

 

From this we can suggest that the suitable areas for control measures might be anywhere that is yellow or bright green, but that the bright green (southern) band is likely to be more difficult to clear. 

 

However, we must also take the biology of the fly into account. Starting at its northern limit the West-African fly belt can be divided in three  bands. A northern band where tsetse distribution is very patchy; a middle band where flies are more evenly spread over the major river systems and finally a southern band where the flies also invade secondary and tertiary tributaries. As you might expect, discrete fly populations, when identified, are more easily dealt with than diffuse populations in the more humid southern parts of the belt. 

 

 

Unfortunately, however, the tsetse fly is a very strong flier, and can move long distances. Therefore cleared areas can easily be reinvaded from neighbouring (uncleared) areas. Arguably, therefore, clearing tsetse from the drier parts might be achieved with minimal risk of reinvasion . Elsewhere, it might prove necessary to maintain a barrier around a controlled area, where flies are continuously being controlled.  

 

 

 

Finally based on the information given above, groups of river basins of different sizes (6,000 kmē, 60,000 kmē, 600,000 kmē) where selected to study the economic feasibility of tsetse eradication. Three sizes of areas were identified: core areas, along the edge of the tsetse belt (in outlined in red); medium sized areas to which projects in the core areas might be expanded (in light blue); and a large area which effectively joins up the medium areas (l dark blue together with brown). The dark green band to the south shows the moister distribution limits of the most important tsetse fly species (Glossina tachnioides), which could be added to the third (large area) if enough resources were available, control of which would effectively lead to the total eradication of the fly from West Africa.

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