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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 />

24

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