Opportunities for the smallholder sandalwood industry in ... - ACIAR
Opportunities for the smallholder sandalwood industry in ... - ACIAR
Opportunities for the smallholder sandalwood industry in ... - ACIAR
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120,000<br />
100,000<br />
Seedl<strong>in</strong>gs planted<br />
80,000<br />
60,000<br />
40,000<br />
20,000<br />
0<br />
Namamau Kauri Natapoa Nangai Mahogany Sandalwood Whitewood<br />
Species<br />
Figure 7.<br />
Seedl<strong>in</strong>gs planted across 15 islands <strong>in</strong> Vanuatu between 2000 and 2006 <strong>for</strong> six <strong>in</strong>digenous (kauri—Agathis<br />
macrophyla, namamau—Flueggea flexuosa, nangai—Canarium <strong>in</strong>dicum, natapoa—Term<strong>in</strong>alia catappa,<br />
<strong>sandalwood</strong>—Santalum, whitewood—Endospermum medullosum) and one exotic (mahogany—Swietenia<br />
mahogany) tree species<br />
All <strong>sandalwood</strong> ga<strong>the</strong>rers were <strong>in</strong>volved <strong>in</strong> <strong>the</strong> trade<br />
and/or plant<strong>in</strong>g of <strong>sandalwood</strong>. It is conspicuous that<br />
60% of <strong>the</strong> households ‘ga<strong>the</strong>r<strong>in</strong>g <strong>sandalwood</strong>’ were<br />
<strong>in</strong>volved exclusively with its plant<strong>in</strong>g. These households<br />
may have fully exploited <strong>the</strong>ir wild custodial<br />
resources and are now <strong>in</strong> <strong>the</strong> process of replant<strong>in</strong>g, or<br />
may be households without any historical ownership<br />
of wild sources of <strong>sandalwood</strong>. While it is not possible<br />
to determ<strong>in</strong>e <strong>the</strong> proportion of <strong>the</strong>se two categories, it<br />
is likely that part of <strong>the</strong> 60% represents a completely<br />
new source of <strong>sandalwood</strong>, which will help <strong>in</strong> distribut<strong>in</strong>g<br />
<strong>the</strong> economic benefits of <strong>the</strong> species more<br />
equitably. Regardless of <strong>the</strong> demographic makeup of<br />
this category, it is encourag<strong>in</strong>g that households plant<strong>in</strong>g<br />
<strong>sandalwood</strong> represent a much greater proportion<br />
than those harvest<strong>in</strong>g <strong>for</strong> sale (Table 1).<br />
Plant<strong>in</strong>g <strong>sandalwood</strong> <strong>in</strong> Vanuatu<br />
Sandalwood occurs naturally on eight ma<strong>in</strong> islands of<br />
Vanuatu (Santo, Malekula, Efate, Erromango, Aniwa,<br />
Tanna, Futuna and Aneityum), but ano<strong>the</strong>r eight<br />
islands have areas with climatic and edaphic conditions<br />
suitable <strong>for</strong> its production (Malo, Aore, Ambae,<br />
Pentecost, Ambrym, Epi, Paama and Shepherd)<br />
(Gillieson et al. 2008). The latter eight islands, all<br />
north of <strong>the</strong> central island of Efate, have little to no<br />
planted <strong>sandalwood</strong> established <strong>in</strong> smallhold<strong>in</strong>gs.<br />
Establish<strong>in</strong>g <strong>sandalwood</strong> production over a wide<br />
geographical area will enable <strong>the</strong> Vanuatu <strong><strong>in</strong>dustry</strong><br />
to <strong>in</strong>crease overall volumes.<br />
In recent years, <strong>smallholder</strong>s have begun to plant<br />
<strong>sandalwood</strong> seedl<strong>in</strong>gs <strong>in</strong> garden areas with<strong>in</strong> <strong>the</strong><br />
swidden agricultural system; <strong>the</strong>se trees persist <strong>in</strong><br />
<strong>the</strong> regenerated <strong>for</strong>est after <strong>the</strong> garden is abandoned.<br />
Early growth of <strong>sandalwood</strong> trees <strong>in</strong> such systems is<br />
greater <strong>in</strong> newly established than <strong>in</strong> older (3–4-yearold)<br />
gardens. Sandalwood seedl<strong>in</strong>gs are also be<strong>in</strong>g<br />
established <strong>in</strong> native <strong>for</strong>ests as enrichment plant<strong>in</strong>gs<br />
and with<strong>in</strong> <strong>the</strong> village as ‘specimen’ plant<strong>in</strong>gs.<br />
Between 2000 and 2006, <strong>the</strong> annual plant<strong>in</strong>g rate<br />
was 14,270 <strong>sandalwood</strong> trees (99,890 trees <strong>in</strong> total),<br />
which was significantly (P < 0.05) greater than <strong>for</strong><br />
<strong>the</strong> previous 7 years (1993–99) when <strong>the</strong> annual<br />
plant<strong>in</strong>g rate was 478 trees (3,346 trees <strong>in</strong> total)<br />
(Figure 8). There<strong>for</strong>e, 96% of <strong>the</strong> <strong>sandalwood</strong> plant<strong>in</strong>gs<br />
recorded <strong>in</strong> <strong>the</strong> 2006 survey occurred between<br />
2000 and 2006 (Figure 9). These were established<br />
by 305 <strong>smallholder</strong>s, with an average of 327 trees<br />
per <strong>smallholder</strong> (Table 2). Approximately 86% of <strong>the</strong><br />
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