Plants Pterostylis pulchella Recorded in Reserves Vulnerable n/a Plants Pterostylis saxicola Not recorded in reserves Endangered n/a Plants Rhizanthella slateri Not recorded in reserves Endangered n/a Plants Sarcochilus weinthalii Not recorded in reserves Vulnerable n/a Plants Thelymitra sp. kangaloon Not recorded in reserves Critically Endangered n/a Plants Olearia cordata Not recorded in reserves Vulnerable n/a Plants Ozothamnus vagans Not recorded in reserves Vulnerable n/a Plants Lychnothamnus barbatus Not recorded in reserves Endangered n/a Plants Macrozamia cardiacensis Not recorded in reserves n/a Vulnerable Plants Macrozamia conferta Recorded in Reserves Vulnerable Vulnerable Plants Macrozamia cranei Not recorded in reserves Endangered Endangered Plants Macrozamia elegans Not recorded in reserves n/a Endangered Plants Macrozamia fawcettii Recorded in Reserves n/a Near Threatened Plants Macrozamia flexuosa Recorded in Reserves n/a Endangered Plants Macrozamia humilis Not recorded in reserves n/a Vulnerable Plants Macrozamia occidua Not recorded in reserves Vulnerable Vulnerable Plants Macrozamia viridis Not recorded in reserves n/a Endangered Plants Hibbertia marginata Not recorded in reserves Vulnerable n/a Plants Astrotricha roddii Not recorded in reserves Endangered n/a Plants Epacris sparsa Not recorded in reserves Vulnerable n/a Plants Melichrus sp. newfoundland state forest Not recorded in reserves Endangered n/a Plants Styphelia perileuca Not recorded in reserves Vulnerable n/a Plants Leucopogon exolasius Recorded in Reserves Vulnerable n/a Plants Acacia courtii Not recorded in reserves Vulnerable n/a Plants Acacia flocktoniae Recorded in Reserves Vulnerable n/a Plants Acacia macnuttiana Not recorded in reserves Vulnerable n/a Plants Almaleea cambagei Not recorded in reserves Vulnerable n/a Plants Desmodium acanthocladum Not recorded in reserves Vulnerable n/a Plants Phyllota humifusa Recorded in Reserves Vulnerable n/a
Management recommendations Purchase remnants into reservation. Fence remnants and manage public access (especially near residential areas). Exclude access of vehicles and trail bikes for recreational use, and keep pets on leashes. Do not allow removal of fallen timber, bush rocks and leaf litter. Avoid mowing/slashing of understorey to promote regeneration of native species. Reduce spray drift in adjacent paddocks. Encourage wise usage in adjacent lands to ensure water tables are not affected. Implement stock management plans for roadside verges and crown land where grazing is permitted. Ensure local flora species are planted for any revegetation and recovery actions. Re-introduce habitat features (e.g. rocks, logs) at disturbed sites. Natural fire intervals are likely to be several decades to a few hundred years. Repeated hazard reduction burns or too-frequent wildfire impact on vegetation health and regeneration capacity. Provide maps of remnants to local and state Rural Fire Services. Manage fuel loads in surrounding areas, to minimise the risk of inappropriate fire regimes affecting remnants. Ensure chemicals or other mechanisms used to eradicate weeds do not have an adverse affect on remnants. Tropical or sub-tropical rainforest vegetation profile 48.07% Remaining Commonly species within this community Araucaria cunninghamii; Argyrodendron trifoliolatum; Waterhousea floribunda; Baloghia inophylla; Acmena smithii; Choricarpia subargente; Dissiliaria baloghioides; Livistona australis; Pittosporum undulatum, tree-fern; Notelaea venosa; Clerodendrum tomentosu; Adiantum formosum; Asplenium attenuatum; Pellaea; Doodia asper; fern; tussock grass. Management recommendations
Encourage uptake of conservation agreements and covenants on private land. Create buffer zones of native vegetation around remnants that are adjacent to areas. Fence off remnants that are adjacent to residential areas and limit access for vehicles and pets. Protect fallen timber, paddock trees and large trees. Purchase remnants into reservation to increase connectivity. Ensure that livestock are excluded from remnants, through exclusion fencing or barriers. Ensure nearby eucalypt plantations do not impact on groundwater supplies. Increase connectivity between remnants. Plant local indigenous rainforest species, especially key canopy tree species. Discourage the use of fire as a to control lantana or other weeds in or near to rainforest remnants. Plantations also increase wildfire potentials. Remnants can be better protected if surrounded by buffers of indigenous plantings (with canopy, midstorey and understorey species). Ensure that managed fires and, where possible, wildfires do not enter buffer zones around remnants. Implement staged removal of camphor laurel (Cinnamomum camphora). Avoid clearing camphor laurel using heavy machinery. Monitor for early weed detection and eradication. Eucalyptus woodlands with a shrubby understorey vegetation profile 60.12% Remaining Commonly found species within this community Eucalyptus rossii; Eucalyptus crebra; Eucalyptus gummifera; Eucalyptus racemosa; macrorhyncha; Corymbia trachyphloia; Allocasuarina littoralis; eptospermum sp; Leptospermum trinervium; Banksia spinulosa; Entolasia stricta; Microlaena stipoides; Aristida queenslandica; Melichrus urceolatus; Monotoca scoparia; Themeda triandra; Imperata cylindrica; Echinopogon caespitosus; Lomandra multiflora; tussock fern. Management recommendations Encourage uptake of conservation agreements and covenants on private land. Do not allow removal of fallen timber and bush rocks. Manage grazing practices including avoiding set stocking. Avoid fertiliser drift from adjacent crops and pastures. Fence paddock trees to enable natural regeneration. Construct artificial shade for stock. Encourage natural regeneration through fencing and stock management. Replant vegetation using locally-sourced seed.