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Baobab Monograph.pdf - Crops for the Future

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2.2.3 Seed dispersal and tree regeneration<br />

When fruits fall in <strong>the</strong> field, <strong>the</strong> woody outside fractures and termites enter<br />

to eat <strong>the</strong> sweet pulp, thus freeing <strong>the</strong> seeds. A range of animals carry seeds<br />

away from <strong>the</strong> trees: Wickens (1982) records monkeys, squirrels and rats;<br />

and fruits are widely eaten by humans and a number of large animals such as<br />

elephants and elands as well as birds.<br />

Fruits can also be dispersed by water systems and this is important when<br />

considering <strong>the</strong> disjunct distribution of <strong>the</strong> genus and <strong>the</strong> distribution<br />

patterns of A. digitata (see Chapter 3).<br />

African baobab is characteristic of thorn woodlands of <strong>the</strong> savannahs and<br />

fears have been expressed that severe droughts of recent years have affected<br />

regeneration. Equally significant was a tendency to eliminate baobab when<br />

near cotton and cocoa production areas in West Africa because baobab is<br />

known to be an alternative host <strong>for</strong> pests affecting <strong>the</strong>se crops and <strong>the</strong>re was<br />

also a fear of certain cocoa viruses in <strong>the</strong> 1950s. In Eastern Africa, reduction<br />

in populations of baobab have been considered a result of increased elephant<br />

browsing in national parks.<br />

Surprisingly little is known about natural regeneration rates, but to a large<br />

degree this could be because seedlings are not readily recognised since <strong>the</strong>y<br />

lack <strong>the</strong> obvious palmately digitate leaves and swollen trunks. Additionally<br />

<strong>the</strong> association of baobab with <strong>the</strong> farmed parklands or savannah (plate 30)<br />

is a deliberate association with <strong>the</strong> agricultural environment because of <strong>the</strong><br />

tree uses, and regeneration may well depend on trees being deliberately<br />

planted near settlements. A study in Burkina Faso clearly points in this<br />

direction (Gijsbers et al., 1994). This probably marks a change from <strong>the</strong> past,<br />

when rural settlements could well have been made in areas where baobabs<br />

were naturally frequent, as postulated by Wickens. Artificial planting is also<br />

noted by Giffard (1974) in Senegal and by Sidibé et al. (1996) in Mali (plate<br />

32).<br />

For <strong>the</strong> above reasons, many populations are near to villages or exist as<br />

relicts from old human habitation patterns. Young trees respond well to<br />

transplanting. In <strong>the</strong> past some ethnic groups in Mali such as <strong>the</strong> Dogon,<br />

Kagolo and Bambara used to take cuttings from <strong>the</strong> wild and transplant <strong>the</strong>m<br />

around <strong>the</strong>ir villages. The Dogon people used to transplant <strong>the</strong>m next to <strong>the</strong>ir<br />

toilets where <strong>the</strong>y could use wastewater to enable better growth of baobab.<br />

This practice originated from <strong>the</strong> shortage of water at certain times of <strong>the</strong><br />

year and also a scarcity of wild seedlings: <strong>the</strong> germination rate of <strong>the</strong> hard<br />

seeds is usually less than 20% (Danthu et al., 1995). In addition, <strong>the</strong><br />

regenerated plants must be protected from wandering animals during <strong>the</strong> dry<br />

season. Using rigid stakes or fences ensures this protection. Ef<strong>for</strong>ts are<br />

22

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