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Tamarind monograph.pdf - Crops for the Future

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and Madagascar (Bayala et al., 2003). The role of <strong>the</strong> species as a<br />

component of agrosilvopastoral land use in Sahelian villages has been<br />

recorded (Slingerland and Kresson, 2001).<br />

Little is known about tamarind as a component of secondary <strong>for</strong>est<br />

associations, its ability to regenerate naturally, nor whe<strong>the</strong>r <strong>the</strong>re are distinct<br />

eco-geographical populations (see section 5.2.1.3). A survey of existing<br />

ecological community data <strong>for</strong> Africa in this respect could be helpful.<br />

Tesfaye et al., (2001) described <strong>the</strong> vegetation of <strong>the</strong> Gambella Region of<br />

South-eastern Ethiopia and a characteristic tamarind plant association was<br />

affiliated to o<strong>the</strong>rs of <strong>the</strong> Sudanian region. Gashaw et al. (2002) noted that<br />

periodic bush fires seemed to stimulate natural regeneration of tamarind.<br />

De<strong>for</strong>estation has led to a degree of erosion of tamarind, <strong>for</strong> example in<br />

Malawi (Maliro and Kwapata, 2002).<br />

In o<strong>the</strong>r parts of <strong>the</strong> world protection of <strong>the</strong> species by people is also<br />

apparent, <strong>for</strong> example, in <strong>the</strong> Ponchicherry region of South India it occurs in<br />

sacred groves (Ramanujam et al., 2003); it is associated with villages in<br />

Orissa, India (Misra and Dash 2000) and in secondary <strong>for</strong>ests in Sri Lanka<br />

and <strong>the</strong> Western Ghats, India, and Gujarat (Hitmayake and Ratnayoke, 2000;<br />

Sharma et al., 1986; Champion, 1936); and in homestead gardens in<br />

Bangladesh (Ahmed and Rahman, 2004).<br />

As a leguminous species <strong>the</strong> degree of nodulation could be a factor<br />

influencing failure to regenerate naturally although <strong>the</strong> genus seemed to<br />

survive as a non-nodulator in South Pakistan (Qadri and Zehra, 2004).<br />

Mycorrhizal associations may be equally important (see Chapter 5).<br />

Seedlings prefer soils with organic matter available <strong>for</strong> early growth<br />

(Aubreville, 1950), and Thiyageshwari et al. (2003) confirmed <strong>the</strong> need <strong>for</strong><br />

nutrients during <strong>the</strong> nursery stage to raise sturdy tamarind plants <strong>for</strong><br />

af<strong>for</strong>estation; root length appears to be critical in <strong>the</strong> early growth stages.<br />

4.5 Pollen and seed dispersal<br />

The presence of nectar in <strong>the</strong> tamarind flower suggests that pollination is<br />

carried out by insects (Prasad, 1963; FAO, 1988). The structure of <strong>the</strong> flower<br />

however does not exclude <strong>the</strong> possibility of self-pollination, which can also<br />

result in seed set.<br />

The large, hard seeds are dispersed by both animals and man. When <strong>the</strong><br />

fruits are eaten fresh, <strong>the</strong> seeds are often discarded (Bettencourt et al., 1999).<br />

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