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Summary
of the final report on the Australian Flora Foundation funded project:
Reproductive biology and improvement of Australian tropical
sandalwood (Santalum lanceolatum)
Tony Page
School of Marine and Tropical Biology, James Cook University, Cairns, Queensland
4870 September 2010 Grant
details Final
report
In
Queensland, sandalwood (S. lanceolatum) has long been commercially
exploited for its powdered heartwood used in funeral pyres and
insence. Harvesting natural sources of sandalwood in Cape York commenced after 1900 and continued
until the early 1930’s, stimulated mainly by demand
from China. With recent identification of high quality S. lanceolatum in Cape
York (Page et al. 2007) there is opportunity to develop this resource
for commercial agroforestry plantings. This
will depend on the development of forms suited to commercial production,
with high growth rates yielding high volumes of heartwood containing
concentrated oils with high levels of a- and ß-santalol.
The
implementation of a successful breeding programme for any sandalwood
species will depend upon knowledge of its breeding system and its crosscompatibility
with related species that are a source for
potentially useful characters. Given also the continued exploitation
of S.
lanceolatum in Queensland,
a knowledge of its breeding system will assist those developing
strategies aimed at conserving current wild populations and establishing
new plantings within its natural distribution. Information on
the breeding system and patterns of gene flow are important for planning
germplasm collection, designing and managing seed orchards and for
maintaining genetic diversity in breeding populations The objectives
of the present study
were to determine levels of (i) self- and (ii) cross-compatibility within Santalum
lanceolatum, S.
album and S. austrocaledonicum and (iii) cross-compatibility
between these three sandalwood species.
Santalum lanceolatum may be considered to have a facultative
allogamous (incomplete
outbreeding) breeding system. This study found variation between genotypes
in the level putative self-incompatibility, where some (20%) were found
to set seed following self-pollination, while the remaining 80%
had no seed development with such pollinations. However, a significantly
greater proportion of genotypes developed seed following intraspecific
cross pollination (62%) compared with selfpollination (20%). In accession
2 where sufficient self and
cross pollinations were performed no significant difference were
found between them percentage seed set. The seed set from self-pollination
were successfully germinated and have been growing for 2 years
without any substantial morphological distinction between inbred and outcrossed seedlings.
While total geographic isolation and significant morphological divergence
exists between S. lanceolatum with each of S. album and S.
austrocaledonicum this study found no indication of
reproductive barrier(s) between them. No significant differences
were found in the percentage seed set among S.
lanceolatum intraspecific crosses (7.5%) compared
with reciprocal S.
lanceolatum x S. austrocaledonicum interspecific
crosses (7.6%). Germination of seed derived from intraspecific outcross pollinations
was found to be low (41%) relative to interspecific pollinations with
each of S. album (114% - with many seeds producing two
seedlings) and S. austrocaledonicum (70%). Therefore
while seed set from intraspecific outcross pollinations was greater
than for reciprocal S.
lanceolatum x S. album crosses (4.3%), no
significant differences were found for the percentage of seedlings developed
from these two pollination types (2.5% and 4.8% respectively).
The results of this study have implications for both the domestication
of S. lanceolatum for its commercial production and for conservation of its
natural stands.
The use of genetic variation present within the high quality S. album and S.
austrocaledonicum could be used for the improvement of S. lanceolatum and vice
versa. However, inappropriate planting of foreign each of these species
within the their natural ranges is likely to result in gene exchange among them
and affect the
genetic integrity of these natural populations.
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