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 />
establishment conditions <strong>and</strong> l<strong>and</strong> use practices. Shade <strong>and</strong> ornamental plantings, particularly in school<br />
grounds, have acted as centres for dispersal, with greatest concentration of the species within 2 km of these<br />
centres at the time of his study. Firth found that red krasnozem soils were the preferred substrate, <strong>and</strong><br />
ab<strong>and</strong>oned banana plantations were frequently seen to be ready colonisation sites. Localities with the greatest<br />
cover were centred in old banana plantations at Upper Coopers Creek, The Pocket, Possum Creek <strong>and</strong><br />
Wilsons Creek, mostly on valley sides adjacent to me<strong>and</strong>ering creeks. Each of these areas had their source in<br />
old planted trees in school grounds.<br />
These general patterns can be discerned again in the results of this study, but differences in the methodologies<br />
between the two mapping exercises do not permit detailed or quantitative comparisons.<br />
Firth (1979) noted that the lowl<strong>and</strong> areas of <strong>Byron</strong> <strong>Shire</strong> were colonised widely, perhaps because the red<br />
krasnozem alluvium may be more suited to establishment of Camphor Laurel than the yellow earth <strong>and</strong><br />
chocolate soil alluvium in similar environments elsewhere.<br />
Firth also found that no Camphor Laurel had invaded the eucalypt wet sclerophyll forest vegetation on the<br />
Nightcap, Gibbergunyah <strong>and</strong> Koonyum Ranges. Most of these forests were outside the study area, but the<br />
mapping of 601 ha of eucalypt spp. <strong>and</strong>/or Brush Box Lophostemon confertus + Camphor Laurel (Table 4.4)<br />
in this study may be indicative of increasing invasion of Camphor Laurel into sclerophyll forests. Recent<br />
observations suggest that in the hinterl<strong>and</strong> Camphor Laurel is readily establishing in wet sclerophyll forest<br />
with a sparse understorey. This is particularly evident beneath roost sites of the Topknot Pigeon <strong>and</strong>/or Pied<br />
Currawong (Hank Bower, pers. comm).<br />
4.6.4 Abundance <strong>and</strong> distribution of old growth eucalypt forest<br />
Old growth eucalypt forests have significant habitat value for hollow-dependent Threatened fauna species.<br />
These include Stephen’s B<strong>and</strong>ed Snake, the large forest owls <strong>and</strong> a number of arboreal marsupials <strong>and</strong><br />
microchiropteran bats (Section 6).<br />
The extent of senescence in crowns of eucalypts, as assessed from API, shows that most of the <strong>Shire</strong>’s<br />
eucalypt-dominated forest has little or no old growth component (Table 4.6), reflecting a history of logging,<br />
clearing or inappropriate fire regimes.<br />
Table 4.6 Old growth eucalypt forest - % of eucalypt crowns showing senescence<br />
% of eucalypt crowns showing area (ha) % of % of <strong>Shire</strong><br />
senescence eucalypt (NP, NR<br />
dominated <strong>and</strong> SF)<br />
vegetation<br />
30% 510.27 13.32 0.99<br />
TOTAL 3829.92 100.00 7.44<br />
A map of eucalypt old growth (Map 5) shows areas with high old growth values bordering Mount Jerusalem<br />
National Park. Small areas with intermediate old growth values include the Taylors Lake-Broken Head area,<br />
bordering Tyagarah Nature Reserve, Brunswick Heads, Marshalls Creek <strong>and</strong> around Goonengerry.<br />
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