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A review of dipterocarps - Center for International Forestry Research

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Seed Handling 80<br />

Table 3. Mean insect infestation statistics <strong>for</strong> species received<br />

at Kew (Tompsett and Kemp 1996a, b).<br />

Genus Mean<br />

percent<br />

infestation<br />

more recently, species with OLDA seeds have been<br />

considered. Successful long-term storage has been<br />

achieved in the case <strong>of</strong> some OLDA species.<br />

In the case <strong>of</strong> recalcitrant seeds, some methods<br />

currently available are useful to ensure the survival <strong>of</strong><br />

seed material during extended field collection trips, <strong>for</strong><br />

planting and <strong>for</strong> storage in the short to medium term.<br />

However, the methods cannot ensure a continuous supply<br />

<strong>of</strong> planting materials throughout the long periods when<br />

mother trees are not fruiting.<br />

Work on dipterocarp seed storage is <strong>review</strong>ed in the<br />

Seed Physiology chapter but some practical storage<br />

methods are briefly discussed.<br />

Imbibed Storage in Media such as Sawdust,<br />

Perlite and Vermiculite<br />

Storage <strong>of</strong> recalcitrant dipterocarp seeds in sawdust,<br />

ground charcoal, perlite and vermiculite has been<br />

employed to maintain high moisture content. This is the<br />

most commonly used method <strong>for</strong> prolonging recalcitrantseed<br />

viability. With care, seeds can be kept viable in this<br />

way <strong>for</strong> several months. Table 4 shows some <strong>of</strong> the work<br />

carried out on imbibed storage but the limitations <strong>of</strong> the<br />

method are:<br />

a) a proportion <strong>of</strong> the seeds may germinate due to the<br />

high moisture content under these conditions; and<br />

b) in many cases, because <strong>of</strong> the difficulties in<br />

controlling aeration and moisture content, necrosis<br />

may occur and microbial infection may set in; seed<br />

viability is then severely affected.<br />

Storage in Airtight Containers<br />

Dry seeds <strong>of</strong> the OLDA type have been successfully<br />

stored in airtight containers. For example, Dipterocarpus<br />

intricatus has been retained <strong>for</strong> 2829 days with no loss<br />

<strong>of</strong> viability observed (Tompsett and Kemp 1996a, b).<br />

Storage under a partial vacuum has been attempted<br />

<strong>for</strong> seeds <strong>of</strong> the recalcitrant species Shorea robusta at<br />

15°C (Khare et al. 1987); 54% viability after a period<br />

<strong>of</strong> 49 days in storage was reported, beyond which further<br />

storage resulted in the death <strong>of</strong> most <strong>of</strong> the seeds.<br />

Un<strong>for</strong>tunately, moisture content was not measured during<br />

storage so the extent to which this factor contributed to<br />

viability loss is unknown. Seed storage in airtight<br />

containers is not appropriate <strong>for</strong> recalcitrant-seeded<br />

species as it leads to an increasing depletion <strong>of</strong> oxygen<br />

in the containers, associated with progressive loss <strong>of</strong><br />

viability.<br />

Storage in Inflated Bags with Different Gaseous<br />

Environments<br />

Sasaki (1980), working on recalcitrant-seeded<br />

<strong>dipterocarps</strong> <strong>of</strong> Malaysia, reported that ventilation with<br />

ambient air was essential <strong>for</strong> dipterocarp seeds to<br />

preserve viability. For example, he found that the viability<br />

<strong>of</strong> S. roxburghii (syn. S. talura) seed could be prolonged<br />

to seven months with adequate ventilation.<br />

Table 4. Examples <strong>of</strong> optimum recorded storage in various media <strong>for</strong> imbibed seed <strong>of</strong> recalcitrant-seeded Shorea,<br />

Hopea and Parashorea species.<br />

MC: moisture content.<br />

Number <strong>of</strong><br />

species<br />

examined<br />

Number <strong>of</strong><br />

species<br />

infested<br />

Dipterocarpus 35 10 10<br />

Shorea 16 18 12<br />

Hopea 8 5 4<br />

Parashorea 4 2 2<br />

Dryobalanops 1 3 1<br />

Species Source<br />

Optimum storage recorded<br />

Days Temp.<br />

( o C)<br />

Germination<br />

(%)<br />

MC<br />

(%)<br />

Medium<br />

Shorea platyclados Tang (1971) 20 16 64 27 Vermiculite<br />

Hopea ferrea Tompsett (1992) 300 16 40 30-50 Mainly perlite<br />

Parashorea smythiesii Tompsett (1992) 317 18 46 45 Perlite<br />

Shorea fallax Tompsett (1992) 50 21 50 40 Sawdust

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