Byron Flora and Fauna Study 1999 - Byron Shire Council
Byron Flora and Fauna Study 1999 - Byron Shire Council
Byron Flora and Fauna Study 1999 - Byron Shire Council
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A GREENPRINT FOR A SUSTAINABLE FUTURE<br />
Durobby (Syzygium moorei FAMILY MYRTACEAE)<br />
Introduction. Durobby (also known as Coolamon) is a highly ornamental tree which has a restricted distribution in<br />
lowl<strong>and</strong> rainforests of southeast Queensl<strong>and</strong> <strong>and</strong> northeast New South Wales. It is well known in the <strong>Byron</strong> <strong>Shire</strong>, with<br />
conspicuous specimens occurring along the Brunswick River, in the coastal reserves <strong>and</strong> scattered as isolated paddock<br />
trees <strong>and</strong> in small remnants. Its name is reflected in the Coolamon Scenic Drive which transverses the <strong>Shire</strong> <strong>and</strong> the<br />
Coolamon Villa at Mullumbimby. It is widely planted as a street tree <strong>and</strong> ornamental. No recovery plan has been prepared<br />
for Durobby. A detailed species outline has been compiled by Barry <strong>and</strong> Thomas (1994) (Queensl<strong>and</strong>).<br />
Conservation status. Durobby is listed on Schedule 2 (Vulnerable) of the TSC Act, 1995 <strong>and</strong> has a ROTAP code of 2VCi<br />
(Briggs <strong>and</strong> Leigh 1996).<br />
Habit. A tree attaining a height of 40 m <strong>and</strong> a stem diameter of 60 cm. (Floyd 1989). The tree has dense dark green<br />
foliage.<br />
Flowers. Showy pink flowers are borne on the branches (Harden 1991). Barry <strong>and</strong> Thomas (1994) note that the plant<br />
pollinators of Durobby are unknown. Floyd (1989) records that bees are attracted to the flowers. The cauliflorous<br />
flowering habit is often indicative of bat pollination. Several different pollinators may operate, as in the case of the related<br />
Syzygium cormiflorum in north Queensl<strong>and</strong> (Crome <strong>and</strong> Irvine 1986).<br />
Fruit. Berry white, suffused with green, flattened, globular, fleshy, up to 6-cm diameter. Seeds dull, rough, creamy fawn,<br />
2-3 cm broad, 1.0-1.5 cm thick. Ripe March-May (Floyd 1989). Neither Floyd (1989) nor Holmes (1987) record bird<br />
species as eating the fruit, but seed is likely to be dispersed by the larger fruit pigeons. Seed may also be carried by water.<br />
Habitat. Riverine <strong>and</strong> gully rainforest at low altitude (Floyd 1989).<br />
Distribution. Restricted to the Richmond, Brunswick <strong>and</strong> Tweed Rivers in NSW <strong>and</strong> Upper Mudgeeraba Creek in Queensl<strong>and</strong>.<br />
Recorded in NSW from Emigrant Creek; Hayters Hill; Mullumbimby; Brunswick Heads NR; Crabbes Creek;<br />
Burringbar; Dum Dum; Eungella; Couchy Creek; Durobby Creek; Hogans Scrub (Floyd 1989). Details of 75 locations in<br />
the study area have been compiled, including sixteen new sites found by the authors during this study.<br />
Regeneration <strong>and</strong> horticulture. Germination may take several months (Nicholson <strong>and</strong> Nicholson 1985). Floyd (1989)<br />
suggests that grub attack of seeds may be reduced if collected before fully ripe. Cuttings are successful <strong>and</strong> may be grown<br />
from healthy tip cuttings (Floyd 1989). Natural regeneration of Durobby is only rarely observed throughout the species’<br />
range, <strong>and</strong> the factors that are limiting have not been studied. In the study area <strong>and</strong> surrounds, many trees exist as<br />
remnant paddock trees, where seed dispersal to suitable sites for regeneration is unlikely. Remnant <strong>and</strong> regrowth rainforest<br />
along creeks <strong>and</strong> gullies provides suitable habitat for this species. The best chance for regeneration opportunity is<br />
likely to be in large areas of forest where microsites suiting the requirements of the species at successive lifecycle phases<br />
may be present.<br />
Economic <strong>and</strong> cultural significance. Floyd (1989) notes that little is known about the timber <strong>and</strong> its possible uses. The<br />
species is well known in horticulture. The white fleshy fruits are edible though insipid in flavour (Nicholson <strong>and</strong> Nicholson<br />
1985), <strong>and</strong> were eaten by Aboriginals (Floyd 1989).<br />
Abundance <strong>and</strong> reservation. Durobby is scattered through suitable habitat <strong>and</strong> trees have been retained as ornamental<br />
paddock trees throughout the Tweed <strong>and</strong> Brunswick region. No estimate of numbers has been made. Durobby is reserved<br />
in the <strong>Shire</strong> in the Inner Pocket NR, Billinudgel NR, Brunswick Heads NR, Hayters Hill NR <strong>and</strong> Broken Head NR.<br />
Briggs <strong>and</strong> Leigh (1996) consider that its reservation is inadequate.<br />
Threats <strong>and</strong> amelioration. L<strong>and</strong> clearing <strong>and</strong> weed invasion are listed by Barry <strong>and</strong> Thomas (1994) as threats to Durobby<br />
in Queensl<strong>and</strong>. Poor dispersal <strong>and</strong> lack of regeneration threaten the species, <strong>and</strong> grazing, roadworks, hardwood plantation<br />
establishment, streambank erosion, fire <strong>and</strong> coastal storms are additional threats in NSW.<br />
Although mature trees persist for long periods, opportunities for natural regeneration are limited outside existing rainforest<br />
environments. Seedlings are unlikely to establish in the vicinity of isolated paddock trees <strong>and</strong> regenerating rainforest<br />
in the region is generally suppressed by woody weeds. Much of the well-drained lowl<strong>and</strong>s of the <strong>Shire</strong> would provide<br />
suitable habitat if rehabilitated <strong>and</strong> planted. However, many of these areas consist of prime agricultural l<strong>and</strong> or residential<br />
areas.<br />
To improve the conservation status of Durobby, the health of the population <strong>and</strong> its regeneration potential should be<br />
enhanced by weed management, grazing exclusion, fire protection <strong>and</strong> replanting of surrounding habitat.<br />
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