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A review of dipterocarps - Center for International Forestry Research

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Conservation <strong>of</strong> Genetic Resources in the dipterocarpaceae 48<br />

Table 3. Outcrossing rates <strong>of</strong> Dipterocarps.<br />

Species Outcrossing Rate tm<br />

(± standard error)<br />

tropical tree species (Murawski and Hamrick 1990,<br />

1991). Apparently, the low density <strong>of</strong> trees in logged<br />

stands reduces the inter-tree movement <strong>of</strong> pollinators<br />

and promotes self-pollination. Selfing, in part, may be<br />

aided by a weak self-incompatibility system.<br />

Kitamura et al. (1994) compared outcrossing rates<br />

<strong>of</strong> Dryobalanops aromatica in primary and secondary<br />

<strong>for</strong>ests but found no significant differences.<br />

Self-incompatibility as well as mating system studies<br />

suggest that <strong>dipterocarps</strong> are predominantly outcrossed.<br />

Outcrossing in large populations can allow populations<br />

to harbour considerable genetic variation. In <strong>dipterocarps</strong>,<br />

mass flowering is also likely to enhance outcrossing by<br />

allowing exchange <strong>of</strong> gametes among a very large number<br />

<strong>of</strong> individuals. Not surprisingly, there<strong>for</strong>e, populations<br />

<strong>of</strong> <strong>dipterocarps</strong> show considerable genetic variation (see<br />

below).<br />

Although the analysis <strong>of</strong> mating systems shows that<br />

the rates <strong>of</strong> outcrossing are high, it is also clear that there<br />

is a considerable potential <strong>for</strong> selfing in almost all species<br />

examined so far. Moreover, apomixis has been reported<br />

in several species (see below). While outcrossing<br />

continuously generates new genetic variation, potential<br />

<strong>for</strong> self-pollination and apomixis allows occasional new<br />

variants to spread in the population or colonise new sites,<br />

and thereby promote differentiation <strong>of</strong> taxa.<br />

Pollen and Seed Dispersal<br />

Pollen dispersal influences the mating system, and both<br />

pollen and seed dispersal affect population genetic<br />

structure. Limited dispersal results in inbreeding, small<br />

effective population sizes, and a high level <strong>of</strong><br />

differentiation among populations. Extensive dispersal<br />

has the opposite effect.<br />

Outcrossing in <strong>dipterocarps</strong> is achieved through a<br />

wide variety <strong>of</strong> pollinators that differ in their <strong>for</strong>aging<br />

References<br />

Dryobalanops<br />

0.794 (±0.059) – Kitamura et al. (1994)<br />

aromatica<br />

0.856 (±0.063)<br />

Shorea congestiflora 0.874 (±0.021) Murawski et al. (1994)<br />

S. megistophylla 0.860 (±0.058) Murawski et al. (1994)<br />

S. trapezifolia 0.617 (±0.033) Murawski et al. (1994)<br />

Stemonoporus<br />

0.898 (±0.022) Murawski & Bawa<br />

oblongifolius<br />

(1993)<br />

ranges and there<strong>for</strong>e disperse pollen<br />

over varying distances. Appanah and<br />

Chan (1981) implicated thrips as<br />

pollen vectors <strong>for</strong> several species <strong>of</strong><br />

Malaysian species <strong>of</strong> Shorea, section<br />

Muticae. The thrips breed in flower<br />

buds <strong>of</strong> the species they pollinate and,<br />

as flowering progresses, they multiply<br />

in number. The adult thrips feed on<br />

stamens and petals. As the petals <strong>of</strong> the<br />

flowers are shed from the tree the<br />

thrips fall on the ground and then move<br />

to a new cohort <strong>of</strong> subsequently opened flowers. The<br />

distances over which thrips move are not known but,<br />

because <strong>of</strong> their relatively small body size, they<br />

apparently do not fly over long distances. It is presumed<br />

that their restricted movement is not a drawback in their<br />

effectiveness as pollinators because the species they<br />

pollinate are relatively abundant.<br />

Dayanandan et al. (1990) present evidence <strong>for</strong><br />

pollination <strong>of</strong> Shorea megistophylla (section Doona) and<br />

Vateria copallifera by bees (Apis spp.). They also<br />

observed a wide variety <strong>of</strong> other insect floral visitors<br />

including thrips. However, the thrips acted as flower<br />

predators rather than pollinators, particularly in V.<br />

copallifera.<br />

More recently, Momose et al. (1994) have presented<br />

evidence <strong>for</strong> pollination <strong>of</strong> Dryobalanops lanceolata, a<br />

large canopy tree species in Sarawak, by medium sized,<br />

stingless bees (Trigona spp.). They also noted the presence<br />

<strong>of</strong> many other types <strong>of</strong> flower visitors (Coleoptera and<br />

Diptera). Momose et al. suggest that medium sized,<br />

stingless bees constitute an important group <strong>of</strong> pollen<br />

vectors <strong>for</strong> canopy and subcanopy trees in Sarawak (see<br />

also Chan and Appanah 1980).<br />

Clearly, the <strong>dipterocarps</strong> are pollinated by a wide<br />

variety <strong>of</strong> insects. The three detailed studies, respectively<br />

by Appanah and Chan (1981), Dayanandan et al. (1990),<br />

and Momose et al. (1994) have revealed three different<br />

classes <strong>of</strong> pollinators. Ashton (1982) in his extensive<br />

<strong>review</strong> also lists beetles and moths as flower visitors,<br />

although their role in pollination has not yet been<br />

demonstrated. Among the pollinators implicated so far,<br />

all, except thrips, are capable <strong>of</strong> moving pollen over long<br />

distances. The extent <strong>of</strong> gene flow via pollen (and seeds)<br />

is further discussed in subsequent sections.<br />

Seed dispersal in most <strong>dipterocarps</strong> is by wind<br />

(Ashton 1982). In most species, sepals are modified into

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