Woylie

Description

Bettongia ogilbyi is a species of potoroine marsupial that digs for fungi during the night, usually maintaining a solitary range around a central nest. The length of the head and body combined is 310 to 380 millimetres (12 to 15 in), entirely covered in fur that is a grey-brown over the back, a buff colour across the face, thigh and flank, and blending to the pale cream colour beneath. The greyish brown of the upper-parts of the pelage is interspersed with silvery hair. The tail is a similar length to the head and body, measuring from 290 to 350 mm (11 to 14 in), and is a rufous brown colour that ends in a blackish tip. The upper-side of the slightly prehensile tail has a ridge of longer fur along its length. The average measurements are 330 mm (13 in) for the heady-body length and 310 mm (12 in) for the tail. The average weight is 1,300 grams (46 oz).

This species resembles the burrowing boodie (Bettongia lesueur), although the woylie is distinctly paler at the ventral side, and lacks the blackish colour of the boodie's tail. The ring around the eye of the woylie is pale, and its muzzle is longer and more pointed than the boodie, and less than Gilbert's potoroo (Potorous gilbertii), with which it once shared an overlapping distribution range.

Distribution and habitat

The woylie is known to have once inhabited a wide range of habitats, including low arid scrub or desert spinifex grasslands. The population in south-west Australia persisted into the twentieth century, seemingly surviving the mass extinction of similar mammals in the previous decades, and was collected at temperate locations near Margaret River, by G. C. Shortridge in 1909, and by Charles M. Hoy in 1920. The last collections made at King George Sound and the Denmark regions of Western Australia in the 1930s coincided with the earliest records of the introduced red fox (Vulpes vulpes), which was first seen at Perth in 1927, and in the south not long thereafter.

The dispersal of many potoroine species from their place of birth appears to be by sub-adult males acquiring a new territory. That has been recorded in these species when they reoccupy an area subjected to fire that had killed the previous residents.

Population collapse

The woylie was originally found in great abundance across southern Australia, north to about 30°S, in a wide distribution range from the coast in the west and east toward the Great Dividing Range.

The species was observed at all parts of the Swan River Colony when the field worker John Gilbert visited during its founding years. Gilbert noted woylies on the tidal flats of the Swan Coastal Plain and river itself, and their nests amongst clumps of grass and the hollows of trees, observing a preference for woodlands of Eucalyptus wandoo. As late as 1910, the population was said to be well known in the Australian south-west, and interviews with older residents helped to establish the time and pattern of decline. The sudden demise of local populations near settlements across the state was noticed by the inhabitants, with most vanishing in the 1930s, while some persisted in a few regions until the 1950s.

The last sighting of a woylie, at Bridgetown, Western Australia, was in 1912. In some areas, that was recalled as following the earlier disappearance of the boodie. The decline was probably caused by a number of factors, including the impact of introduced grazing animals, accompanied by land clearance for pastoralism and agriculture. Predation by introduced red foxes and feral cat has undoubtedly been crucial. The introduction of the European rabbit (Oryctolagus cuniculus), may have also placed the population under pressure, especially in arid and semi-arid regions, by direct competition or the degradation of habitat.

By the 1920s, the woylie was extinct over much of its range.

Changed fire regimes might also have played a part. The species suffered localised extinctions throughout its range, and was highly endangered by the 1970s.

Current

As of 2021, there are only two indigenous populations of woylies, one of which is in the Upper Warren region of WA. This group is being monitored by the Department of Biodiversity, Conservation and Attractions, and it has been found that their numbers have risen in the years up to 2021.

Diet

As with the Potoroos and other Bettongia species, the woylie has a largely fungivorous diet and will dig for a wide variety of their fruiting bodies. Although it may eat tubers, seeds, insects, and resin exuded from Hakea laurina, the bulk of its nutrients are derived from underground fungi, which it digs out with its strong fore-claws. The fungi can only be digested indirectly. They are consumed by bacteria in a portion of its stomach. The bacteria produce the nutrients that are digested in the rest of the animal's stomach and small intestine. When it was widespread and abundant, the woylie probably played an important role in the dispersal of fungal spores within desert ecosystems.

The austral summer and autumn seasons provide woylies with the fruiting bodies of hypogeous fungi, and around 24 fungal taxa are known to be consumed. During the summer months, species of the truffle-like Mesophellia form the major part of the diet. The core of the truffles of Mesophellia is consumed by woylies, which avoid the hard outer layer, and has been analysed for its nutritional value. The food is a rich source of lipids and trace elements accumulated by the fungus, and high protein levels that lack the required lycine and other amino acids, may be compensated by fermentation processes on the available aminos cysteine and methionine within the digestion. In other seasons, woylies may adopt a more herbivorous range of foods in addition to that season's hypogeous fungal bodies.

Woylies have been observed eating the large seeds of Australian sandalwood, Santalum spicatum, a nutritious food that the animal is known to place in a shallow cache for later consumption. The habit of caching the seeds is likely to have played an important role in the dispersal of the tree. However, Australian sandalwood was a commercially valuable tree, and was extensively cleared during colonisation. Populations of woylies introduced to an island off the coast of South Australia consume mainly plant material, tubers and roots, seeds and leaves, and beetles, a diet regarded as unusual for the species. Analysis of that colony's diet showed that it included fungal spores, as detected in their scats, although that is likely to have been an occupant of the guts of the beetles.

Ecology

Woylies were well known to the first European settlers of rural Western Australia. The species was used for meat during the earlier colonial period, although that practice did not persist amongst the colonists because, while it was readily available and easily captured, the skinning of the animal is said to be difficult. At one time, woylies were kept as pets in the same region. Although similar species of marsupials were often regarded as agricultural pests, the woylie did not always acquire this reputation, and was sometimes identified as a non-destructive native animal.

Native predators of the woylie include the wedge-tailed eagle (Aquila audax), a large raptor thought to have been a significant influence on their mortality. The red fox (Vulpes vulpes) and feral cat (Felis catus), which arrived with Europeans, are known to prey on this species, and both have been cited as a major cause of local extinctions. Since the control of the red fox, the cat has become the major predator of the species.

Woylies are natural excavators, dubbed an "ecosystem engineer" by one researcher, moving about six tonnes of soil annually in its quest for food. digging up the soil creating seed beds for new seeds and new plants to grow. This turning over of the soil not only spreads the spores of fungi and seeds of other native plants, but provides good beds for these the seeds to grow, so the bushland is kept healthy.

Behaviour

Woylies are largely nocturnal, resting during the day and emerging around dusk rather than after sunset, unlike the strictly nocturnal rufous bettong Aepyprymnus rufescens, although woylies always return to their nests before dawn. They can breed all year round if the conditions are favourable. The female is fertile at six months of age and gives birth every 3.5 months. Its lifespan in the wild is about four to six years.

The woylie builds its dome-shaped nest in a shallow scrape under a bush, and is able to curl its tail to carry bundles of nesting material. The nest, which consists of grass and shredded bark, sticks, leaves and other available material, is well made and discreet.

The species behaves in a characteristic way when disturbed at its nest, rapidly leaving the site with an explosive noise. The body is arched as the animal hops away, with the head held low and the tail extended, using a bipedal motion in lengthy bounds to evade a potential predator.

A broad foraging area is occupied by individuals, with a larger area for the male, and these will likely overlap with the larger range of other woylies. Within the range, each animal defends a smaller central territory which only overlaps between males and females. Several nests within a range may provide casual and communal accommodation; only a central nest site is defended to the exclusion of any other. Measurements of the nest territory and foraging ranges of individuals has given variable results. An early study at an open woodland suggested an area of 15 to 28 hectares around the nest site for the female and 28 to 43 ha for the male. The central range seemed to extend around the nest for 4 to 6 ha. A subsequent survey calculated an exclusive zone around the nest of 2 to 3 ha for the male, and the foraging area as 27 ha for the male and 20 ha for the female. An analysis of a radio-tracking survey also indicated a nest range of 2 to 3 ha, yet a smaller foraging range of 7 to 9 ha for the species.

Conservation

Conservation efforts in the late 20th century concentrated on reintroducing woylies to sites in their former range, after controlling red foxes. By 1992, the woylie was reported from only four small areas in Western Australia. In 1996, it occurred in six sites in Western Australia, including Karakamia Sanctuary, run by the Australian Wildlife Conservancy, and on three islands and two mainland sites in South Australia, following a reintroduction program after foxes had been controlled.

Stable populations were established in places such as Venus Bay, St Peter Island and Wedge Island in South Australia, Shark Bay in Western Australia, and Scotia Sanctuary in New South Wales. As a result of those efforts, the woylie population rose to sufficient numbers that it was taken off the threatened species list in 1996. The total population of the species rose to 40,000 by 2001.

However, another sudden decline occurred in late 2001, and in just five years, the woylie population dropped to only 10–30% of its pre-2001 numbers. It was returned to the IUCN Red List as critically endangered. The exact cause of the rapid population crash was uncertain, although researcher Andrew Thompson found two parasite infestations in woylie blood. Predation and habitat destruction were also suggested as contributing to the decline of the species. In 2011, the global population was estimated to be less than 5,600 individuals. It was hypothesised in 2013 that disease within populations was making them more vulnerable to predation.

By 2010, one of the remaining thriving habitats for the woylie was the Dryandra Woodland south of Perth in Western Australia. The state-sponsored control of foxes offered new hope for the species, but along with the native numbat, numbers were decimated by feral cats, which flourished after fox numbers were brought under control. A major program to control feral cats has seen the number of both woylies and numbats begin to increase, although populations remain vastly reduced from even recent decades. In 2011 the species was reported as living mostly in open sclerophyll forest and Mallee Woodlands and Shrublands eucalypt assemblages, with a dense low understorey of tussock grasses.

Despite those declines, woylies continued as small localised populations in predator-free sanctuaries, including a population established in 2010 at Wadderin Sanctuary in the central Western Australian wheatbelt. The reintroduction of control programs for predators saw the species successfully conserved at sites including Perup, Tutanning and the Dryandra Woodland reserves. In the Dryandra Woodland, woylie numbers, which had been decimated by hundreds of feral cats, were reported to be recovering after the introduction of a state-sponsored cat baiting and trapping program, supported by the adjacent farming community. It was discovered that most of the feral cats were living and breeding on surrounding farms, and then entering the woodland to kill the native animals.

The species has become established at a large fenced reserve at Western Australia's Mount Gibson Sanctuary. It was reintroduced to large fenced landscapes at Newhaven in the Northern Territory in August 2021 and to Mallee Cliffs National Park in NSW in September 2021.

As of 2020, plans were in place to reintroduce the species to the Pilliga Forest in NSW, and to Dirk Hartog Island in WA.

It is a key species in the faunal reconstruction project within the Dhilba Guuranda–Innes National Park on South Australia's Yorke Peninsula, formerly named the Great Southern Ark (2019), renamed Marna Banggara in June 2020 in honour of the Narungga people, who are the traditional owners of the region. As part of this project, the woylie's reintroduction is being supported by large-scale fencing and the baiting of feral cats and foxes. In August 2021, 40 woylies were translocated from Wedge Island to Dhilba Guuranda–Innes National Park. Surveillance trapping in 2022 confirmed population survival and breeding. In July 2022, 36 woylies were translocated from WA for the first time, with the permission of the Noongar traditional custodians, to boost genetic diversity. Another 73 animals were translocated from Dryandra National Park in WA in June 2023, when it was reported that the existing bettongs were surviving and breeding. A trapping survey estimated that there are over 200 in Dhilba Guuranda-Innes National Park as a result of the Marna Banggara project as of March 2023. The species has been listed as near threatened by the IUCN since 2025.