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- Gippsland Basin bioregion
- Context statement for the Gippsland Basin bioregion
- Ecology
- Terrestrial species and communities
Principal vegetation types and distribution patterns
The impact of vegetation clearing in the Gippsland Basin bioregion is evident with 57% of the bioregion covered with non-native vegetation and buildings (Table 20). Of native vegetation identified in the NVIS, 12% of the Gippsland Basin bioregion is covered in eucalyptus tall open forest and open forest with ferns, herbs, sedges, rushes or wet tussock grasses predominately in the east (Figure 44). A large area of open forest is situated in the southern Strzelecki Ranges. The combined eucalyptus open forest categories in Table 20 occupy 23% of the Gippsland Basin bioregion. Collectively, Eucalyptus woodlands occupy a smaller area (8%) but show a high association with palustrine and lacustrine wetlands (16%) compared to eucalyptus open forest (9%);Table 20). Acacia, Melaleuca and Banksia forest or shrublands are associated with marine and estuarine wetlands (12%) as are saline or brackish sedgelands or grasslands (5%).
Figure 44 National Vegetation Information System (NVIS) major vegetation subgroups
Data: Department of the Environment and Water Resources (Dataset 2)
Species and ecological communities of national significance
The EPBC Act lists threatened flora, fauna and ecological communities under a number of classifications. In the Gippsland Basin bioregion the common classifications and their definitions include:
- Critically Endangered: species face a high risk in the wild of extinction in the immediate future
- Endangered: species face a high risk in the wild of extinction in the near future
- Vulnerable: species face a high risk in the wild of extinction in the medium-term future.
Approximately 24 flora species are nationally protected, with six classified as Endangered and 15 as Vulnerable (Table 22).
Within the fauna biodiversity asset group (Table 22), a total of 45 fauna species are listed as threatened including frogs (one Endangered, four Vulnerable), bats (one Vulnerable), fish (two Vulnerable), invertebrates (one Vulnerable), mammals (six Endangered, five Vulnerable), marine birds (two Endangered, six Vulnerable), waders (one Vulnerable), passerine birds (two Endangered), non-passerine birds (one Critically Endangered, three Endangered, two Vulnerable) waders (one Vulnerable) and reptiles (one Endangered, one Vulnerable).
The Orange-bellied Parrot (Neophema chrysogaster), endemic to southern Australia, is the only Critically Endangered species thought to occur in the Gippsland Basin bioregion in association with Jack Smith Lake, indicating potential water dependence.
The importance of the natural diversity maintained within Wilsons Promontory National Park is highlighted with designation of the National Park as a UNESCO biosphere reserve in 1981. Diverse vegetation communities exist which include warm temperate and cool temperate rainforest, tall open forests (Eucalyptus spp.), woodlands, heathlands, swamp and coastal communities including mangroves (Parks Victoria, 2002). Three threatened fauna species and three flora species occur within Wilsons Promontory National Park (species name identified with c in Table 22) and one EPBC Act listed migratory species, Sanderling (Calidris alba).
Threatened ecological communities
Ecological communities consist of a naturally occurring group of animals, plants or other biota that interact in a unique habitat. There are 12 EPBC Act listed threatened ecological communities (not shown) in the East and West Gippsland Catchment Management Authorities, however, only four are likely to occur in the Gippsland Basin bioregion (Table 22). Three communities are Critically Endangered including the ecologically significant Gippsland Red Gum (Eucalyptus tereticornis subsp. mediana) Grassy Woodland and Associated Native Grassland. One community, the Subtropical and Temperate Coastal Saltmarsh, is listed as Vulnerable.
The Gippsland Red Gum Grassy Woodland and Associated Native Grassland community is endemic to the region and nationally important as a temperate grassland and grassy woodland ecosystem. Temperate grassland ecosystems are poorly preserved and conserved nationally, and their decline in Gippsland is largely due to land clearing (DEWHA, 2010). The community provides habitat to other threatened flora and fauna and is known to be rich in wildflowers and other plant species (DEWHA, 2010). The association of this vegetation community with water bodies (Table 20) suggests some level of water dependency.
Species of regional significance
Victoria’s Flora and Fauna Guarantee Act 1988 (the FFG Act) provides the statutory mechanism for the conservation of flora and fauna that are threatened in the state. In the Gippsland Basin bioregion, 41 flora species are listed as Threatened (FFG Act) of which 16 are listed as Endangered and 11 as Vulnerable (the EPBC Act) (Table 22).
Threatened fauna species total 35 and include four frogs, one bat, two fish, one invertebrate, nine mammals, eight marine birds, two passerine birds, six non-passerine birds, one wader and two reptiles. Many of the FFG Act listed fauna species are also EPBC Act listed (Table 22).
The Victorian Department of Environment, Land, Water and Planning (DELWP) Threatened Species Advisory List is an additional non-statutory state listing of importance to planning processes. Approximately 32 flora species are listed as Endangered and 70 as Vulnerable. There are ten fauna species that are listed as Critically Endangered, 15 are listed as Endangered and 12 listed as Vulnerable.
Threatened ecological communities
State ecological vegetation community mapping (Native Vegetation-Modelled 2005 Ecological Vegetation Classes (EVC)) identifies 629,569 ha of vegetation communities in the Gippsland Basin bioregion of which 139,906 ha (22%) have a Victorian Bioregional Conservation Status of Vulnerable and 100,775 ha (16%) are Endangered (Figure 45). Broad EVC groups that are Endangered include riparian scrubs or swamp scrubs and woodlands (31,000 ha), plains woodlands and forest (including grasslands, 25,000 ha) and damp forests (24,000 ha). Many other Endangered EVC groups exist within the bioregion, but cover much smaller areas. Lowland forest (51,000 ha), plains woodlands and forest (including grasslands, 30,000 ha) are considered Vulnerable. Approximately 12,000 ha of wetland species are also threatened.
Data: Department of Environment and Primary Industries (Dataset 4)
Threatening processes
The following potentially threatening processes were collated under the FFG Act. Processes such as alteration to natural flow regimes of rivers and streams, collection of native orchids, degradation of native riparian vegetation along rivers and streams, and fragmentation of habitat are pertinent threats. Introduced plants and animals threaten both terrestrial and aquatic systems through outcompeting and damaging or destroying native biodiversity. In coastal areas, dune degradation resulting from vegetation removal and human impacts threaten biodiversity. In aquatic systems, water quality is threatened by agricultural practices and erosion mechanisms (landslips, gully, sheet rill and river bank erosion) generating sediment and nutrient movement into waterways. In such instances, stream ecology is altered impacting flora and fauna. Grazing or altered hydrology also results in loss of fringing wetland vegetation. Further land clearing poses a major threat to bioregional habitats and biodiversity.
Table 22 Species and ecological communities within the Gippsland Basin bioregion listed as threatened nationally under the Commonwealth’s Environment Protection and Biodiversity Conservation Act 1999 (the EPBC Act). State-listed threatened species under Victoria’s Flora and Fauna Guarantee Act 1988 (the FFG Act) are indicated with a box
Biodiversity asset group |
Scientific name |
Common name |
Status under the EPBC Act |
Status under the FFG Act |
Water dependence |
Comments on water dependence |
---|---|---|---|---|---|---|
Plants |
||||||
Acacia caerulescens |
Limestone Blue Wattle |
Vulnerable |
■ |
Possible |
Wide range of habitats - often grows close to rivers, lakes and roads |
|
Acacia maidenii |
Maiden’s Wattle |
na |
■ |
Likely |
Grows at the outer margin of floodplains |
|
Acronychia oblongifolia |
Yellow-wood |
na |
■ |
Possible |
Occurs in and on the margins of warm rainforests |
|
Adiantum diaphanum |
Filmy Maidenhair |
na |
■ |
Likely |
Grows along streams and around waterfalls |
|
Amphibromus fluitans |
River Swamp Wallaby-grass |
Vulnerable |
Likely |
Wetland species |
||
Boronia galbraithiae |
Aniseed Boronia |
Vulnerable |
■ |
Likely |
Maybe facultative |
|
Botrychium australe |
Austral Moonwort |
na |
■ |
Possible |
Wide range of habitats – may be facultative near streams |
|
Caladenia orientalis |
Eastern Spider-orchid |
Endangered |
■ |
Unlikely |
Grows in well-drained soils |
|
Caladenia peysleyi |
Heath Spider-orchid |
na |
■ |
Unknown |
NA |
|
Caladenia tessellataac |
Thick-lipped Spider-orchid |
Vulnerable |
na |
Unlikely |
Grows in well-drained sand/clay loam in heath or grassy woodlands |
|
Caladenia valida |
Robust Spider-orchid |
na |
■ |
Unknown |
NA |
|
Cardamine tryssa |
Dainty Bitter-cress |
na |
■ |
Unknown |
NA |
|
Craspedia canens |
Grey Billy-buttons |
na |
■ |
Possible |
Grows in wet and dry situations May be facultative |
|
Cryptostylis erecta |
Bonnet Orchid |
na |
■ |
Likely |
Found along creek lines and rhizomes. Need to be moist at all times |
|
Cryptostylis hunteriana |
Leafless Tongue-orchid |
Vulnerable |
■ |
Likely |
Grows in swampy heaths |
|
Cullen parvum |
Small Scurf-pea |
na |
■ |
Possible |
Appears to require winter flooding |
|
Cyathea cunninghamii |
Slender Tree-fern |
na |
■ |
Likely |
Grows in deep gullies beside creeks |
|
Cyathea leichhardtiana |
Prickly Tree-fern |
na |
■ |
Possible |
Occurs on mountain slopes near creeks |
|
Dianella amoena |
Matted Flax-lily |
Endangered |
■ |
Possible |
Grows in well-drained to seasonally wet soils in lowland grassland, grassy woodland, valley grassy forest and creeklines |
|
Diuris punctata var. punctata |
Purple Diuris |
na |
■ |
Possible |
May be facultative – occurs in association with red gum and swamp gum |
|
Dodonaea procumbens |
Trailing Hop-bush |
Vulnerable |
na |
Possible |
Grows in low-lying, often winter wet locations |
|
Eucalyptus strzeleckii |
Strzelecki Gum |
Vulnerable |
■ |
Likely |
Seasonal waterlogging |
|
Grevillea celata |
Colquhoun Grevillea |
Vulnerable |
■ |
Unlikely |
Occurs in dry schlerophyll woodland and heathy open forest |
|
Hakea macraeana |
Willow Needlewood |
na |
■ |
Possible |
Found in understorey of wet or dry sclerophyll forest, drought resistant |
|
Isopogon prostratus |
Prostrate Cone-bush |
na |
■ |
Unlikely |
Occurs in heath on plateaux and ridges or dry open eucalypt woodland |
|
Lachnagrostis punicea subsp. filifolia |
Purple Blown-grass |
na |
■ |
Likely |
Occurs in wet marshes and slightly saline swamps and depressions |
|
Lindsaea trichomanoides |
Oval Wedge-fern |
na |
■ |
Unknown |
Found on dry sites in lowland to montane forest/shrubland |
|
Livistona australis |
Cabbage Fan-palm |
na |
■ |
Likely |
Often in swampy sites |
|
Nematolepis frondosa |
Leafy Nematolepis |
Vulnerable |
■ |
Unlikely |
Varied habitats including rocky outcrops and tall open forest |
|
Pomaderris vacciniifolia |
Round-leaf Pomaderris |
na |
■ |
Likely |
Found along creek lines |
|
Prasophyllum correctum |
Gaping Leek-orchid |
Endangered |
■ |
Unlikely |
Grows in freely draining soils |
|
Prasophyllum frenchiic |
Maroon Leek-orchid |
Endangered |
■ |
Likely |
Occurs in swampland |
|
Prasophyllum spicatum |
Dense Leek-orchid |
Vulnerable |
na |
Likely |
Seasonal waterlogging |
|
Prostanthera galbraithiae |
Wellington Mint-bush |
Vulnerable |
■ |
Unlikely |
NA |
|
Pseudoraphis paradoxa |
Slender Mud-grass |
na |
■ |
Likely |
Grows in and around pools and watercourses |
|
Pterostylis baptistii |
King Greenhood |
na |
■ |
Likely |
Grows in moist to wet soils |
|
Pterostylis chlorogramma |
Green-striped Greenhood |
Vulnerable |
■ |
Possible |
Occurs in moist well-drained soils |
|
Pterostylis cucullataac |
Leafy Greenhood |
Vulnerable |
■ |
Likely |
Inland populations occur on river banks or alluvial floodplains. Coastal populations grow in seasonally damp, well-drained sandy loams |
|
Pterostylis lustra |
Small Sickle Greenhood |
na |
■ |
Likely |
Restricted to swampy areas |
|
Pterostylis tenuissima |
Swamp Greenhood |
Vulnerable |
na |
Likely |
Based on naming |
|
Rulingia prostratab |
Dwarf Kerrawang |
Endangered |
■ |
Likely |
Associated with wetland margins |
|
Sambucus australasica |
Yellow Elderberry |
na |
■ |
Possible |
Grows on the edges of rainforests and widespread in coastal districts |
|
Symplocus thwaitesii |
Buff Hazelwood |
na |
■ |
Likely |
Grows alongside Snowy River |
|
Thelymitra epipactoidesb |
Metallic Sun-orchid |
Endangered |
■ |
Unlikely |
NA |
|
Thelymitra incurva |
Swamp Sun-orchid |
na |
■ |
Possible |
Grows in heathlands and heathy woodlands mostly around the edges of grasstree plains |
|
Xerochrysum palustreb |
Swamp Everlasting |
Vulnerable |
■ |
Likely |
Grows in wetlands, seen growing in water 1 m deep |
|
Frogs |
|
|||||
Heleioporus australiacus |
Giant Burrowing Frog |
Vulnerable |
■ |
Likely |
NA |
|
Litoria aureab |
Green and Golden Bell Frog |
Vulnerable |
na |
Likely |
NA |
|
Litoria littlejohni |
Large Brown Tree Frog |
Vulnerable |
■ |
Likely |
NA |
|
Litoria raniformisab |
Southern Bell Frog |
Vulnerable |
■ |
Likely |
NA |
|
Litoria spenceri |
Spotted Tree Frog |
Endangered |
■ |
Likely |
NA |
|
Bats |
|
|||||
Pteropus poliocephalus |
Grey-headed Flying-fox |
Vulnerable |
■ |
Likely |
NA |
|
Fish |
|
|||||
Galaxiella pusilla |
Dwarf Galaxias |
Vulnerable |
■ |
Likely |
NA |
|
Prototroctes maraenaa |
Australian Grayling |
Vulnerable |
■ |
Likely |
NA |
|
Invertebrates |
|
|||||
Megascolides australis |
Giant Gippsland Earthworm |
Vulnerable |
■ |
Likely |
NA |
|
Mammals |
|
|||||
Arctocephalus tropicalis |
Sub-antarctic Fur-Seal |
Vulnerable |
na |
Likely |
NA |
|
Dasyurus maculatusc |
Spot-tailed Quoll |
Endangered |
■ |
Likely |
NA |
|
Eubalaena australisa |
Southern Right Whale |
Endangered |
■ |
Likely |
NA |
|
Gymnobelideus leadbeateri |
Leadbeater’s Possum |
Endangered |
■ |
Likely |
NA |
|
Isoodon obesulus obesulus |
Southern Brown Bandicoot (Eastern) |
Endangered |
■ |
Likely |
NA |
|
Megaptera novaeangliae |
Humpback Whale |
Vulnerable |
■ |
Likely |
NA |
|
Mirounga leonina |
Southern Elephant Seal |
Vulnerable |
na |
Likely |
NA |
|
Potorous longipes |
Long-footed Potoroo |
Endangered |
■ |
Likely |
NA |
|
Potorous tridactylus tridactylusc |
Long-nosed Potoroo |
Vulnerable |
■ |
Likely |
NA |
|
Pseudomys fumeus |
Smoky Mouse |
Endangered |
■ |
Likely |
NA |
|
Pseudomys novaehollandiaec |
New Holland Mouse |
Vulnerable |
na |
Likely |
NA |
|
Marine birds |
|
|||||
Diomedea exulans (sensu lato) |
Wandering Albatross |
Vulnerable |
■ |
Likely |
NA |
|
Halobaena caerulea |
Blue Petrel |
Vulnerable |
na |
Likely |
NA |
|
Macronectes giganteus |
Southern Giant-Petrel |
Endangered |
■ |
Likely |
NA |
|
Macronectes halli |
Northern Giant-Petrel |
Vulnerable |
■ |
Likely |
NA |
|
Phoebetria fusca |
Sooty Albatross |
na |
■ |
Likely |
NA |
|
Thalassarche bulleri |
Buller's Albatross |
Vulnerable |
■ |
Likely |
NA |
|
Thalassarche carteri |
Indian Yellow-nosed Albatross |
na |
■ |
Likely |
NA |
|
Thalassarche cauta cautaa |
Shy Albatross |
Vulnerable |
■ |
Likely |
NA |
|
Thalassarche chrysostoma |
Grey-headed Albatross |
Endangered |
■ |
Likely |
NA |
|
Thalassarche melanophris |
Black-browed Albatross |
Vulnerable |
na |
Likely |
NA |
|
Passerine birds |
|
|||||
Anthochaera phrygia |
Regent Honeyeater |
Endangered |
■ |
Likely |
NA |
|
Dasyornis brachypterus |
Eastern Bristlebird |
Endangered |
■ |
Likely |
NA |
|
Non-passerine birds |
|
|||||
Botaurus poiciloptilus |
Australasian Bittern |
Endangered |
■ |
Likely |
Nests in swamps |
|
Calyptorhynchus banksii graptogyne |
Red-tailed Black-Cockatoo (south-eastern) |
Endangered |
■ |
Likely |
NA |
|
Lathamus discolora |
Swift Parrot |
Endangered |
■ |
Likely |
NA |
|
Neophema chrysogastera |
Orange-bellied Parrot |
Critically Endangered |
■ |
Likely |
NA |
|
Polytelis swainsonii |
Superb Parrot |
Vulnerable |
■ |
Likely |
NA |
|
Rostratula australis |
Australian Painted Snipe |
Vulnerable |
■ |
Likely |
NA |
|
Waders |
|
|||||
Sternula nereis nereis |
Australian Fairy Tern |
Vulnerable |
■ |
Likely |
NA |
|
Reptiles |
|
|||||
Dermochelys coriaceaa |
Leathery Turtle |
Endangered |
■ |
Likely |
NA |
|
Eretmochelys imbricata |
Hawksbill Turtle |
Vulnerable |
na |
Likely |
NA |
|
Ecological communities |
|
|||||
Eucalyptus tereticornis subsp. mediana |
Gippsland Red Gum (Eucalyptus tereticornis subsp. mediana) Grassy Woodland and Associated Native Grassland |
Critically Endangered |
na |
Likely |
Some location near water bodies |
|
|
Littoral Rainforest and Coastal Vine Thickets of Eastern Australia |
Critically Endangered |
na |
Likely |
NA |
|
|
Seasonal Herbaceous Wetlands (Freshwater) of the Temperate Lowland Plains |
Critically Endangered |
na |
Likely |
Wetland environment |
|
|
Subtropical and Temperate Coastal Saltmarsh |
Vulnerable |
na |
Likely |
Some groundwater connection |
Data: Department of Environment and Primary Industries (Dataset 5)
na – Not applicable as species is not listed
NA – Data related to water dependence are not available
a - Species occurs at Corner Inlet Ramsar site
b - Species occurs at the Gippsland Lakes Ramsar site
c - Species occurs at Wilsons Promontory National Park
