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Overview of timber demand and supply on Leyte Island ... - UQ eSpace

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Socio-ec<strong>on</strong>omic Factors Affecting Smallholder Tree Planting <str<strong>on</strong>g>and</str<strong>on</strong>g> Management Intenti<strong>on</strong>s<br />

most species the resp<strong>on</strong>dents intend to plant are classified as high-valued <str<strong>on</strong>g>timber</str<strong>on</strong>g> species<br />

or fruit trees.<br />

Table 4. Number <str<strong>on</strong>g>of</str<strong>on</strong>g> trees proposed for planting<br />

Species name<br />

Number <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

households<br />

Number <str<strong>on</strong>g>of</str<strong>on</strong>g><br />

stems<br />

Distributi<strong>on</strong><br />

ratio (%)<br />

Mahogany (Swietenia macrophylla) 49 10,520 34.7<br />

Gmelina (Gmelina arborea) 33 8,989 29.6<br />

Mangium (Acacia mangium) 19 4,533 14.9<br />

Bagras (Eucalyptus deglupta) 15 1,909 6.3<br />

Mango (Mangifera indica) 15 1,647 5.4<br />

Ipil-ipil (Leucaena leucocephala) 2 1,025 3.4<br />

Molave (Vitex parviflora) 12 285 0.9<br />

Lanz<strong>on</strong>es (Lansium domesticum) 6 205 0.7<br />

Jackfruit (Artocarpus heterophyllus) 4 180 0.6<br />

Narra (Pterocarpus indicus) 7 161 0.5<br />

Others 18 873 2.9<br />

Total 95 30,327 100.0<br />

Proporti<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> trees intended to plant (%) Proporti<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> households (%)<br />

Percentage<br />

80.0<br />

70.0<br />

60.0<br />

50.0<br />

40.0<br />

30.0<br />

20.0<br />

10.0<br />

0.0<br />

≥ 1,000 ≥ 500 ≥ 100 ≥ 50 ≥ 0<br />

Range <str<strong>on</strong>g>of</str<strong>on</strong>g> the number <str<strong>on</strong>g>of</str<strong>on</strong>g> trees intended to plant<br />

Figure 1. Distributi<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> the number <str<strong>on</strong>g>of</str<strong>on</strong>g> trees intended for planting across households<br />

To predict growers’ preferences for tree species in the future, the 27 species were classified<br />

into five categories as presented in Table 5. The classificati<strong>on</strong> adopted here follows the<br />

percepti<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> local community people. High-valued species are used for building<br />

c<strong>on</strong>structi<strong>on</strong>, furniture, poles <str<strong>on</strong>g>and</str<strong>on</strong>g> piles, while n<strong>on</strong>-high-valued species are used mainly for<br />

firewood, charcoal <str<strong>on</strong>g>and</str<strong>on</strong>g> light-fencing. As indicated in the table, most species the resp<strong>on</strong>dents<br />

intend to plant are classified as high-valued <str<strong>on</strong>g>timber</str<strong>on</strong>g> species or fruit trees.<br />

Table 6 reports the number <str<strong>on</strong>g>of</str<strong>on</strong>g> trees <str<strong>on</strong>g>of</str<strong>on</strong>g> each species category to be planted in the future in<br />

total across the resp<strong>on</strong>dents. The most preferred species category was found to be the n<strong>on</strong>native<br />

high-valued <str<strong>on</strong>g>timber</str<strong>on</strong>g> species. These species might be preferred due to the direct<br />

availability <str<strong>on</strong>g>of</str<strong>on</strong>g> their seedlings (Gregorio et al. in process) or their shorter rotati<strong>on</strong> period as<br />

compared to native high-valued species. On the other h<str<strong>on</strong>g>and</str<strong>on</strong>g>, it is obvious that the<br />

resp<strong>on</strong>dents had little interest in planting n<strong>on</strong>-high-valued species, native or n<strong>on</strong>-native. It is<br />

28

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