Island just off the southern coast of Australia

Including the Mount Lofty Ranges, surrounding lowlands, and offshore Kangaroo Island, this ecoregion is mostly vegetated by eucalypt woodlands. A number of unique ecosystems are found here, but clearing has been widespread, with only fragmented vegetation remaining. The native fauna of this region has been widely affected by loss of habitat and fragmentation. Numerous local mammalian and avian extinctions have occurred in this ecoregion, and continued clearance and invasive species are threats.

  • Scientific Code
  • Ecoregion Category
  • Size
    9,200 square miles
  • Status
  • Habitats

Location and General Description
The Mount Lofty Woodlands Ecoregion forms a relatively narrow strip along the Mount Lofty Ranges, and their foothills and valleys. The ranges intercept the humid southwesterly winds that predominate during the winter, creating a mediterranean-type climate. The main factors that determine vegetation structure are rainfall, disturbance, and soil characteristics. The rainfall ranges from nearly 900 mm in the higher peaks of the southern Mount Lofty Ranges to below 400 in the northern Mount Lofty Ranges (Boardman 1986). The ancient geology of the region resulted in fairly weathered soils (Oades 1986).

The region encompasses a range of vegetation types including sclerophyll woodlands, open and grassy woodlands, and grasslands. The woodlands are dominated by different species of Eucalyptus, changing according to rainfall distribution (Paton et al. 1999). The understorey is rich in species from the Myrtaceae, Proteaceae, Mimosaceae (genus Acacia in particular), Fabaceae, and Epacridaceae. Orchids are also well represented. Mallee eucalypt communities are dominated by white mallee (Eucalyptus diversifolia), commonly growing with E. rugosa on the mainland, and also found on Kangaroo Island. Open forests of brown stringybark (E. baxteri), messmate stringybark (E. obliqua), long-leaved box (E. goniocalyx), and/or manna gum (E. viminalis) grow in the Mt. Lofty ranges (Paton et al. 1999). Messmate stringybark may grow in pure stands in areas with high rainfall, reaching heights of 25 m (Beadle 1981). Moving to lower elevations, grassy woodlands of South Australian blue gum (E. leucoxylon) and manna gum grow on heavy soils. At still lower elevations, grey box (E. microcarpa), peppermint box (E. odorata), and mallee box (E. porosa) grow (Paton et al. 1999). Grasslands are dominated by species of Austrostipa and Austrodanthonia (Poaceae), and Lomandra (Liliaceae) (Moore 1970).

The western half of Kangaroo Island is largely dominated by a mixture of open forest and woodlands. Vegetation communities include areas of sugar gum (Eucalyptus cladocalyx) and drooping sheoak (Allocasuarina verticillata), as well as other mixed eucalypt woodlands. Mixed eucalypt woodlands include pink gum (E. fasciculosa), brown stringybark, messmate stringybark, manna gum, and river red gum (E. camaldulensis). Understories are normally dense and shrubby, with Melaleuca spp., Hakea rostrata, and Callistemon rugulosus (Paton et al. 1999).

Biodiversity Features
This region is characterized less by its degree of endemism than by its peculiar combination of biota (Specht 1972). As one of the mediterranean climate environments in Australia, this region shares biological components with the western mediterranean-type ecoregions, and with the southeastern ecoregions, resulting in unique biological assemblages. Several of these components are represented by disjunct populations, most likely genetically isolated, and often in their extreme range of their distribution (Boardman 1986). Within the ecoregion Kangaroo Island stands out as the area with the highest species level endemism (36 species, some 5 percent of the flora) (Davies 1992). Endemic species include E. remota, Adenanthos sericea, A. terminalis, and Petrophile multisecta (Beadle 1981).

Almost all the medium sized marsupials (e.g. bettongs (Betongia spp) and quolls (Dasyurus spp.)) have become extinct in the region (Short and Smith 1994, Strahan 1998). In South Australia, a significant proportion of extinctions have occurred in the temperate woodlands. While the echidna (Tachyglossus aculeatus) is still found throughout the region, the platypus (Ornithorhynchus anatinus) is restricted to Kangaroo Island. Paton et al. (2001) list the current status of mammal species throughout this ecoregion. Eight species, many of them globally threatened, are now locally extinct from the Mount Lofty Ranges portion of this ecoregion alone. Species extirpated from the Mount Lofty Ranges include the eastern quoll (Dasyurus viverrinus), red-tailed phascogale (Phascogale tapoatafa), the extinct eastern hare wallaby (Lagorchestes leporides), tammar wallaby (Macropus eugenii), the vulnerable greater bilby (Macrotis lagotis), the endangered western barred bandicoot (Perameles bougainville), the vulnerable burrowing bettong (Bettongia leseur), and brush-tailed bettong (Bettongia pencillata) (Hilton-Taylor 2000, Paton et al. 1999).

Recently, a sharp decline of passerine birds in the region has been reported (Ford et al. 2001). Species that have been extirpated from woodland habitats in the Mount Lofty Ranges include the endangered regent honeyeater (Xanthomyza phrygia), endangered swift parrot (Lathamus discolor), king quail (Coturnix chinensis), brown quail (C. ypsilophora), and azure kingfisher (Alcedo azurea). The glossy black cockatoo (Calyptorhynchus lathami) has been brought to the brink of local extinction by land clearance. Paton et al. (1999) list a number of other species that have declined in woodland habitats and in the heaths and swamplands of the Mount Lofty Ranges. As a result of vegetation clearance, birds may be moving greater distances to obtain food. Banding studies of honeyeaters, lorikeets, and silvereyes showed that birds are moving over 100 km seasonally to exploit food resources (Paton et al. 1999). While there have been local extinctions and precipitous declines of many birds native to this region, only one species extinction has occurred in this ecoregion. The Kangaroo Island emu (Dromaius baudinianus) became extinct in the 1820s as a result of hunting and the burning of habitat (Stattersfield et al. 1998).

Reptiles have fared better than other taxa: of the 57 species found in the temperate woodlands of South Australia, only one is considered nationally endangered. The pygmy blue tongue lizard (Tilqua adelaiensis) was considered extinct, but was recently discovered. However, several species have declining or localized populations in this ecoregion (Paton et al. 1999).

Current Status
The southern and central sections of this region have been thoroughly modified by human activities, particularly since European settlement. The woodlands of the southern Mount Lofty Ranges were extensively cleared for agriculture (Paton et al. 1999), and urban sprawl around Adelaide has claimed remnant vegetation more recently (Krahenbuehl 1996). Less than 4 percent of native vegetation remains on the Adelaide Plains. Clearance has concentrated on lowland areas with higher agricultural potential (Paton et al 1999). The northern section of the ecoregion retains more integrity, in particular along the ranges.

Overall, protected areas are fairly numerous, but small, and several vegetation types are under represented. Across the ecoregion approximately 10 percent of plant species are extinct, endangered, or threatened. A large proportion of these species are endemic to the region. The fauna of this region has suffered severe reductions in its diversity as a result of the destruction of habitats, hunting, and the impact of introduced predators such as foxes (Vulpes vulpes) and cats (Felis catus).

Grazing has heavily impacted remaining native vegetation. Remnant vegetation in this area consists of small fragments, most of them representing regrowth after clearance, and heavily invaded by exotic species. A large portion of remaining vegetation is privately held. The central grasslands have mostly been replaced by agriculture, but temperate grasslands are still found extensively on the top of ranges or rocky outcrops, albeit usually overgrazed and invaded by European annual grasses (Davies 1997). In this area a number of taxa are extinct, endangered, or threatened.

Although only an estimated 35 percent of Kangaroo Island’s original woodland remains, remnant vegetation has been less severely impacted than that in regions with similar clearance. The poor ironstone based soils have discouraged agriculture, and much of the central island was not cleared until after World War II as part of a returned soldiers scheme. Although extensive areas have been cleared in the past century, large areas of vegetation were set aside in protected areas from 1919 onwards. Today, even in regions with extensive clearing, native vegetation persists in a series of ridges, riparian strips, and roadside verges, providing some connectivity between larger fragments (Paton et al. 1999).

Types and Severity of Threats
While the rate of vegetation clearance has abated, the fragmented nature of most of the vegetation remnants pose grave risks for many species of plants and animals. Although fire is a natural disturbance in the original system, it can have devastating consequences on population persistence in isolated patches that are unlikely to be recolonized from nearby populations. The relatively recent introduction of the Phytophtora cinnamomi pathogen also poses a serious threat to vegetation in the higher rainfall sections of the region.

Introduced mammals are problematic on the mainland portion of this ecoregion. Cats, foxes, and rabbits (Oryctolagus cuniculus) are common throughout the Mount Lofty Ranges and portions of this ecoregion further north. Unlike mainland Australia, Kangaroo Island is not severely affected by introduced grazers. There are no rabbits on the island, and feral goats (Capra hircus) and pigs (Sus scrofa) have only caused minor problems. However, a population of koalas (Phascolarctos cinereus) that were introduced onto the island in the 1920s have caused significant damage to some woodland communities, especially to manna gum trees. Expansion of feral koala populations in the Mount Lofty Ranges could pose a significant to remaining manna gum vegetation. Elevated western grey kangaroo (Macropus fuliginosus) populations in the Mount Lofty Ranges may be affecting native vegetation composition (Paton et al. 1999).

Justification of Ecoregion Delineation
The Mount Lofty Woodlands ecoregion comprises one IBRA, ‘Lofty Block’ (Thackway and Cresswell 1995). Original vegetation consisted of eucalypt open forests and woodlands and heath. This ecoregion is part of the ‘South-east Australia’ Endemic Bird Area (Stattersfield et al. 1998).

Beadle, N. C. W. 1981. The Vegetation of Australia. Cambridge University Press, Cambridge, United Kingdom.

Boardman, R. 1986. The history and evolution of South’s Australia’s forests and woodlands. Pages 16-32 in H. R. Wallace, editor. The ecology of the forests and woodlands of South Australia Woolman Goverment Printer, Adelaide, Australia.

Davies, R. J. P. 1992. Threatened plant species of the Murray Mallee, Mount Lofty Ranges, and Kangaroo Island regions of South Australia. Nature Conservation Society of South Australia. Adelaide, Australia.

Davies, R. J. P. 1997. Weed management in temperate grasslands and box grassy woodlands in South Australia. Black Hill Flora Centre, Adelaide, Australia.

Ford, H. A., G. W. Barrett, D. A. Saunders, and H. F. Recher. 2001. Why have birds in the woodlands of southern Australia declined? Biological Conservation 97: 71-88.

Hilton-Taylor, C. 2000. The IUCN 2000 Red List of Threatened Species. IUCN, Gland, Switzerland and Cambridge, United Kingdom.

Kraehenbuehl, D. 1996. Pre-European vegetation of Adelaide: a survey from Gawler River to Hallett Cove. Nature Conservation Society of South Australia, Adelaide, Australia.

Moore, M. 1970. South-eastern temperate woodlands and grasslands. Pages 169-189 in M. Moore, editor. Australian Grasslands. Australian National University Press, Canberra, Australia.

Oades, J. M. 1986. Water and soils. Pages 44-53 in H. R. Wallace, editor. The ecology of the forests and woodlands of South Australia Woolman Goverment Printer, Adelaide, Australia.

Paton, D.C., A. M. Prescott, R. J. P. Davies, and L. M. Heard. 1999. The distribution, status, and threats to temperate woodlands in South Australia. Pages 57 – 85 in R. J. Hobbs and C. J. Yates, editors. Temperate Eucalypt Woodlands in Australia: biology, conservation, and restoration. Surrey Beatty & Sons, Chipping Norton, Australia.

Short, J. and A. Smith. 1994. Mammal decline and recovery in Australia. Journal of Mammalogy 75: 288 – 297.

Stattersfield, A. J., M. J. Crosby, A. J. Long, and D. C. Wedge. 1998. Endemic Bird Areas of the World. Priorities for biodiversity conservation. BirdLife Conservation Series No. 7. BirdLife International, Cambridge, United Kingdom.

Strahan, R. editor. 1998. The mammals of Australia. Australian Museum/Reed New Holland. Syndey, Australia.

Thackway, R. and I. D. Cresswell. editors. 1995. An Interim Biogeographic Regionalisation for Australia: a framework for establishing the national system of reserves, Version 4.0. Australian Nature Conservation Agency, Canberra.

Prepared by: Jose Facelli
Reviewed by: