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 />
However, examples of listed species occurring in <strong>Byron</strong> <strong>Shire</strong> are provided.<br />
Species classified as ‘depleted habitat/sparse’ (Sheringham <strong>and</strong> Westaway 1995, Table 5.3) occurring in<br />
<strong>Byron</strong> <strong>Shire</strong> include Leafy Twig-rush Cladium procerum, Spider Lily Crinum pedunculatum, Burny Bean Mucuna<br />
gigantea, Myoporum boninense subsp. australe, Milkbush Neisosperma poweri, a grass Panicum paludosum <strong>and</strong> the<br />
epiphytic orchid Peristanthus hillii.<br />
Taxa presumed to be regionally extinct include the perennial herb Knoxia sumatrensis (recorded only once<br />
near Mullumbimby in 1897), Plinanthesis urvillei (a grass recorded from Billinudgel in 1922) <strong>and</strong> Caladenia<br />
quadrifaria (an orchid that occurs in sclerophyll forest <strong>and</strong> was recorded from Brunswick Heads in 1942)<br />
(Sheringham <strong>and</strong> Westaway 1995). Sometimes plants presumed to be extinct have been overlooked or their<br />
presence, although known to local naturalists, has not been reported to the relevant authorities (NSW<br />
NPWS or the NSW Herbarium). Chiloglottis diphylla was presumed to be regionally extinct although local<br />
orchid experts were aware of the plant’s continued presence in <strong>Byron</strong> <strong>Shire</strong> <strong>and</strong>, in fact, now consider the<br />
species to be relatively common (John Moye, pers. comm).<br />
Disjunct taxa (Sheringham <strong>and</strong> Westaway 1995, Table 5.3) occurring in <strong>Byron</strong> <strong>Shire</strong> are Large-leaved Banksia<br />
Banksia robur, Christmas Bells Bl<strong>and</strong>fordia gr<strong>and</strong>iflora <strong>and</strong> Leptomeria drupacea.<br />
Taxa occurring in <strong>Byron</strong> <strong>Shire</strong> <strong>and</strong> that reach their northern or southern geographical limits in Upper<br />
North East NSW (e.g. White Ash Alphitonia petriei, Austromyrtus sp. A, Ferny-leaved Bosistoa Bosistoa pentacocca<br />
<strong>and</strong> Thick-leaved Croton Croton acronychioides) are considered ‘regionally significant’ (Sheringham <strong>and</strong><br />
Westaway 1995).<br />
Species that reach their northern or southern geographical limits within <strong>Byron</strong> <strong>Shire</strong> are of local <strong>and</strong> regional<br />
significance. Such species include Marblewood Acacia bakeri (southern limit at Federal), Blush Coondoo<br />
Planchonella laurifolia (southern limit at the Orara Bridge on the Brunswick River), Comesperma sphaerocarpum<br />
(northern limit at Koonyum Range Rd, Mt Jerusalem N.P), Smooth Parrot-pea Dillwynia glaberrima (northern<br />
limit at Taylor’s Lake south of <strong>Byron</strong> Bay) <strong>and</strong> Slender Yellow-eye Xyris gracilis subsp. gracilis (northern limit<br />
south of Broken Head).<br />
Many of the plants listed as Threatened species or ROTAP species (e.g. Hairy Qu<strong>and</strong>ong, Red-fruited<br />
Ebony, Crystal Creek Walnut) also reach their southern limits within upper north-eastern NSW <strong>and</strong> are<br />
therefore of regional significance in addition to having Threatened species status.<br />
5.5.3 Reservation adequacy<br />
Table 5.7 indicates the occurrence of Threatened species in the <strong>Shire</strong>’s National Parks <strong>and</strong> Nature Reserves.<br />
However, except where populations of 1000 plants are known to be reserved, reservation is considered<br />
inadequate or unknown (Table 5.2). The declaration of new National Parks <strong>and</strong> Nature Reserves in <strong>Byron</strong><br />
<strong>Shire</strong> may strengthen the reservation status of some Threatened species. Information on current reservation<br />
status of Threatened species is available from NSW NPWS.<br />
With two exceptions, all the <strong>Shire</strong>’s Threatened species are considered to be inadequately reserved within<br />
formal conservation reserves (ROTAP codes Table 5.6). Inadequate representation in reserves is a major<br />
criterion for listing as ‘Endangered’ (Briggs <strong>and</strong> Leigh 1996) since threatening processes are more frequently<br />
unmanaged on non-reserved l<strong>and</strong>.<br />
Adequate reservation of habitat for many of the <strong>Shire</strong>’s Threatened species is often not possible since so<br />
much of the coastal lowl<strong>and</strong>s has been cleared. To avoid local, regional or national extinction of these<br />
species, it is therefore essential that they are conserved effectively wherever they occur in the study area.<br />
Protection measures such as fencing, fire management <strong>and</strong> weed control can be put in place <strong>and</strong> will allow<br />
other l<strong>and</strong> uses to proceed along with effective conservation.<br />
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