Overview

Brief Summary

Biology

Burrowing bettongs are strictly nocturnal and use scent to locate food, which they then dig out of the ground using their muscular limbs. This species feeds on tubers, bulbs, seed nuts, plants and fungi, termites and marine refuse (4). Burrowing bettongs have also been observed eating carrion and raiding vegetable gardens (4). Social groups consist of one male and several females. They dig and occupy a simple burrow which may have a short tunnel and 1-2 entrances or a large warren with more than 100 entrances. One of these warrens may house more than 50 individuals from several groups. Males are aggressive towards other males and defend the females in their group (4). Females produce up to three litters each year with one offspring per litter, though twins are occasionally born. Females will mate again shortly after giving birth. However, the second offspring is not born for around four months as embryonic development is delayed. This allows the first-born to be nurtured by the mother and gives it a better chance of survival (4). If the first young dies, embryonic development of the following offspring begins. Gestation lasts for only 21 days, and sexual maturity is attained within one year (4).
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Comprehensive Description

Description

The burrowing bettong is a marsupial and the only burrowing member of the kangaroo family (4) (5) though, as its other common name, the Lesueur's rat kangaroo, indicates, it actually bears some resemblance to a rat. Originally there were two subspecies, Bettongia lesueur graii and Bettongia lesueur nova, though the former subspecies is now Extinct (1). Like a kangaroo, it has well developed, muscular hind limbs and short muscular forearms. The head is small with a pointed muzzle, short rounded ears and beady black eyes (6). This mammal is covered in short dense hair which is brown to grey in colour, and has been described as 'woolly' as its hair is softer than that of other bettong species. Burrowing bettongs also bear a faint hip stripe on the body and a distinctive white tail-tip (2).
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Distribution

Range Description

This species is endemic to Australia, where it was formerly widespread in central, southern, and south-western parts of the country. While it is now presumed to be extinct on the Australian mainland, it persists in insular populations on Bernier and Dorre Islands in Shark Bay (Western Australia) and on Barrow Island off the Pilbara coast (Western Australia) (Richards 2005; Burbidge and Short 2008).

There are reintroduced populations on Faure Island in Shark Bay and Boodie Island (both Western Australia), as well as on the mainland in Scotia Wildlife Sanctuary (New South Wales), Arid Recovery Reserve at Roxby Downs (South Australia), and Heirisson Prong (Western Australia) (all three mainland sites are fenced reserves within the historical range of the species).
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Geographic Range

Bettongia lesueur was once one of the most widespread mammals inhabiting the Australian mainland. It could be found in all suitable habitats throughout mainland Australia, yet by the early 1960’s had become extinct on the mainland and could only be found on the Australian islands of Bernier and Dorre in Shark Bay, and Boodie Island and Barrow Island near the Pilbara coast. Burrowing bettongs used to live on Dirk Hartog Island, but have gone extinct from there as well.

Biogeographic Regions: australian (Native )

  • Government of Western Australia, 2006. "Burrowing Bettong (Boodie)" (On-line). Department of Conservation and Land Management. Accessed November 14, 2006 at http://www.calm.wa.gov.au/plants_animals/pdf_files/sp_boodie.pdf.
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Historic Range:
Australia

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Range

This species no longer exists on mainland Australia, and until recently was only found on three islands off the coast of Western Australia: Barrow, Dorre and Bernier Island (4) (5). Following a successful reintroduction by the Australian Wildlife Conservancy (AWC) in 2002, this species is now also found in Faure Island (7).
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Physical Description

Morphology

Physical Description

Burrowing bettongs are small, stocky animals similar to kangaroos. They have weakly prehensile tails that can be used for gathering nest materials. They are the only member of the family Potoroidae to inhabit burrows year round. They are light yellow to grey above, have a grey underbelly, short, rounded ears and thick, lightly haired tails, much like those of kangaroos. Bettongia lesueur has a body length ranging from 370 mm to 400 mm with a 300 mm mean tail length. Body mass is 0.4 to 1.8 kg for males and 0.5 to 1.7 kg for females. Males tend to be larger in mass and other body measurements than females. They move strictly using their hind limbs and only use their fore limbs and tail for support when stationary.

Burrowing bettongs can be distinguished from other bettongs mainly by their behavior, but also by their coloration. They often have a light yellow coloration on top while other species have a light grey coloration. Woylies (Bettongia penicillata), which are similar in appearance to Bettongia lesueur, do not inhabit burrows and are not gregarious. The same is true of northern bettongs (Bettongia tropica). Food habits also differ between Bettongia species. The dental formula of potoroids is 3/1, 1-0/0 2/2, 4/4 = 32-34.

Range mass: 0.4 to 1.8 kg.

Range length: 370 to 440 mm.

Other Physical Features: endothermic ; homoiothermic; bilateral symmetry

Sexual Dimorphism: male larger

  • Massicot, P. 2004. "Burrowing Bettong" (On-line). Animal Info. Accessed November 14, 2006 at www.animalinfo.org/species/bettlesu.htm.
  • Meyers, P. 2001. "Potoroidae" (On-line). Animal Diversity Web. Accessed November 14, 2006 at http://animaldiversity.ummz.umich.edu/site/accounts/information/Potoroidae.html.
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Ecology

Habitat

Habitat and Ecology

Habitat and Ecology
This species is found in arid and semi-arid areas of shrubland and woodland, on sandy or loose soils. Currently it is found in areas with calcrete rock and sandy areas. It is nocturnal and omnivorous, and lives as loose colonies in a complex warren of underground burrows. The females breed throughout the year and usually give birth to a single young three times a year (J. Richards pers. comm.).

Systems
  • Terrestrial
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Habitat

When burrowing bettongs were still thriving on the mainland, their habitat was diverse, including open eucalypt woodland with grass and shrub under story to sand ridge desert. On the islands where they currently exist, they are found in a variety of habitats including areas consisting of shrubs, grasses and herbs. On Bernier and Barrow islands they show no habitat preference. On Dorre Island they prefer coastal dunes and habitats dominated by Triodia. Burrowing bettongs build extensive burrows in areas with stony soils throughout their current distribution, but used to build burrows in sandy soils on the Australian mainland.

Range elevation: 50 (high) m.

Habitat Regions: temperate ; terrestrial

Terrestrial Biomes: desert or dune ; savanna or grassland ; forest ; scrub forest

  • Sander, U., J. Short, B. Turner. 1997. Social organisation and warren use of the burrowing bettong, Bettongia lesueur, (Macropodoidea: Potoroidae). Wildlife Research, 24: 143-157.
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Habitat

This small marsupial inhabits a variety of habitats from spinifex deserts to woodlands (5).
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Trophic Strategy

Food Habits

Burrowing bettongs are generally herbivorous but have been known to eat termites and marine animal carcasses. They concentrate on the green parts of plants, seeds, fruits, nuts, tubers, bulbs, flowers, and fungi. This species is partial to figs when available. They are able to find food using their sense of smell.

Animal Foods: carrion ; insects

Plant Foods: roots and tubers; seeds, grains, and nuts; fruit; flowers

Other Foods: fungus

Primary Diet: herbivore (Folivore , Frugivore , Granivore )

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Associations

Ecosystem Roles

Burrowing bettongs are thought to compete with both black rats (Rattus rattus) and European rabbits (Oryctolagus cuniculus), although recent studies cast doubt on the importance of rabbits in the decline of B. lesueur. Burrows of B. lesueur may be used by western quolls (Dasyurus geoffroii), greater bilbies (Macrotis lagotis), and silver-tail brushtail possums (Trichosurus vulpecula).

  • Robley, A., J. Short, S. Bradley. 2001. Dietary overlap between the burrowing bettong (Bettongia lesueur) and European rabbit (Oryctolagus cuniculus) in semi-arid coastal Western Australia. Wildlife Research, 28: 341-349.
  • Robley, A., J. Short, S. Bradley. 2002. Do European rabbits (Oryctolagus cuniculus) influence the population ecology of the burrowing bettong (Bettongia lesueur)?. Wildlife Research, 29: 423-429.
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Predation

Predation on Bettongia lesueur is extensive and is thought to be the cause of the extinction of the species from the mainland and one island population. Introduced foxes (Vulpes vulpes) were the primary mainland predator of burrowing bettongs. Feral cats are the primary reason for extinction of B. lesueur on Dirk Hartog Island. There is little information on native predators of burrowing bettongs.

Known Predators:

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Life History and Behavior

Behavior

Communication and Perception

Burrowing bettongs locate food using their keen sense of smell. They are also a tactile species, and often dig for food. Bettongia lesueur is a highly vocal species, yet the range of noises or what they mean in a social or defensive context has not yet been determined. They often make grunts, squeaks, and hisses to communicate.

Communication Channels: tactile ; acoustic ; chemical

Perception Channels: visual ; acoustic

  • Menkhorst, P. 2001. A field guide to the mammals of Australia. New York: Oxford University Press.
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Life Expectancy

Lifespan/Longevity

There is little information on the lifespan of B. lesueur, but it is known to usually live three years in the wild.

Range lifespan

Status: wild:
3 (low) years.

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Lifespan, longevity, and ageing

Observations: Little is known about the longevity of these animals, though one wild born specimen lived 9.9 years in captivity (Richard Weigl 2005).
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Reproduction

Reproduction

Mating in B. lesueur is polygynous, with males mating with several females and maintaining harems within their warrens. Both sexes become sexually mature after about five months. Males are aggressive toward one another in defense of females. Females tend to be non-aggressive, but have been observed being aggressive towards females outside of their warrens.

Mating System: polygynous

Bettongs exhibit embryonic diapause. Lactation causes implantation to be delayed. While one young is still in the pouch, another will not be born until the pouch young has either been weaned after 115 days or has been lost. This allows the mother to have three young relying on her at one time: one weaned but still under care, one in her pouch, and one still in development. Oestrous lasts approximately 23 days.

Breeding interval: Breeding occurs throughout the year.

Breeding season: Breeding occurs throughout the year.

Range number of offspring: 1 to 2.

Average number of offspring: 1.

Average gestation period: 21 days.

Average weaning age: 115 days.

Average time to independence: 180 days.

Average age at sexual or reproductive maturity (female): 5 months.

Average age at sexual or reproductive maturity (male): 5 months.

Key Reproductive Features: iteroparous ; year-round breeding ; gonochoric/gonochoristic/dioecious (sexes separate); viviparous ; embryonic diapause

Average birth mass: 0.317 g.

Average gestation period: 21 days.

Average number of offspring: 1.

Average age at sexual or reproductive maturity (female)

Sex: female:
218 days.

Males invest in their young only to the point of protecting their harems. Females carry young in the pouch and care for them until they are weaned, after about 115 days. Joeys accompany their mother in foraging until their independence, near 180 days.

Parental Investment: altricial ; pre-fertilization (Provisioning, Protecting: Female); pre-hatching/birth (Provisioning: Female, Protecting: Female); pre-weaning/fledging (Provisioning: Female, Protecting: Female); pre-independence (Provisioning: Female, Protecting: Female)

  • Government of Western Australia, 2006. "Burrowing Bettong (Boodie)" (On-line). Department of Conservation and Land Management. Accessed November 14, 2006 at http://www.calm.wa.gov.au/plants_animals/pdf_files/sp_boodie.pdf.
  • Massicot, P. 2004. "Burrowing Bettong" (On-line). Animal Info. Accessed November 14, 2006 at www.animalinfo.org/species/bettlesu.htm.
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Evolution and Systematics

Functional Adaptations

Functional adaptation

Foraging aids revegetation: greater bilby
 

The foraging behavior of bilbies helps revegetate arid landscapes by creating pits that naturally catch plant matter, seeds, and nutrients.

           
  "Fertile patches are created and maintained by a combination of physical  and biologically-mediated processes including soil disturbance by  animals. We examined the creation of fertile patches by 4 vertebrates,  the greater bilby Macrotis lagotis, burrowing  bettong Bettongia lesueur, European rabbit Oryctolagus cuniculus, and Gould's sand goanna Varanus gouldii within dunes, ecotones, and swales in a  dunefield in arid South Australia. These animals all create pits when  foraging for subterranean food resources. We hypothesized that 1) the  effect of pits on litter capture would vary among landscapes and animal  species, 2) larger pits would trap more litter and seed, 3) pits would  contain more viable seed than the surrounding matrix, and 4) the effect  of pits on soil chemistry would vary among animal species, and be  greater in landscapes with more finely textured soils. We found that  litter was restricted almost exclusively to the pits, and was greater in  pits with larger openings. Litter capture was greater in ecotones and  dunes than in swales. A total of 1307 seedlings from 46 genera  germinated from litter samples taken from the pits, but no seedlings  emerged from samples taken from soil surrounding the pits. Foraging pits  contained significantly higher levels of total C and N than surrounding  soil, and total C and N concentrations were greatest in swales and  lowest in dunes. Pits contained ca 55% more mineralisable N that surface  soils, and pits constructed by bilbies and bettongs contained half the  concentration of mineralisable N as those of rabbits and goannas.  Concentrations of mineral N and mineralisable N were also greatest in  the swales. Our results demonstrate the importance of animal-created  pits as nutrient sinks and sites for seedling establishment, and suggest  that changes in the composition of arid zone vertebrates may have  resulted in profound changes to nutrient and soil dynamics in arid  Australia." (James et al. 2009:723)
  Learn more about this functional adaptation.
  • James AI; Eldridge DJ; Hill BM. 2009. Foraging animals create fertile patches in an Australian desert shrubland. Ecography. 32(5): 723 - 732.
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Conservation

Conservation Status

IUCN Red List Assessment


Red List Category
NT
Near Threatened

Red List Criteria

Version
3.1

Year Assessed
2008

Assessor/s
Richards, J., Morris, K. & Burbidge, A.

Reviewer/s
Lamoreux, J. & Hilton-Taylor, C. (Global Mammal Assessment Team)

Contributor/s

Justification
Listed as Near Threatened because its extent of occurrence is small and it is known from just 6-8 locations, making it close to qualifying for Vulnerable under criterion B1. The natural populations of this species are considered stable and reintroduced populations are increasing, habitat for the species is considered stable, and although there are major threats potentially from introduced predators, fire, and disease, this species has genuinely improved in status since the prior assessment. The species occurs naturally on 3 islands, and has been introduced to another 5 localities. There is, however, uncertainty as to whether 2 of these reintroduction sites can be counted as "self-sustaining", and thus be included in the number of locations used in the assessment. This species is also close to qualifying as having "extreme fluctuations" in population, which would also qualify it for a threatened category.

History
  • 1996
    Vulnerable
    (Baillie and Groombridge 1996)
  • 1994
    Endangered
    (Groombridge 1994)
  • 1990
    Rare
    (IUCN 1990)
  • 1988
    Rare
    (IUCN Conservation Monitoring Centre 1988)
  • 1986
    Rare
    (IUCN Conservation Monitoring Centre 1986)
  • 1982
    Rare
    (Thornback and Jenkins 1982)
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Conservation Status

Due to extinction from the mainland of Australia Bettongia leseur has been listed under the IUCN Red List as Vulnerable. Numbers on Barrow island are near 5,000. The species is listed in Appendix I of CITES. It is considered endangered by the US Fish and Wildlife Srevice.

Reasons for the decline of burrowing bettongs have been attributed to predation by introduced foxes and feral cats. Competition from rabbits and black rats is also one reason for population declines due to reduced food availability. Fire regimes that reduced vegetation of lowland shrubs, which is the primary food source of this species, along with human hunts to reduce crop predation have contributed to the decline of populations.

US Federal List: endangered

CITES: appendix i

State of Michigan List: no special status

IUCN Red List of Threatened Species: near threatened

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Current Listing Status Summary

Status: Endangered
Date Listed: 12/02/1970
Lead Region: Foreign (Region 10) 
Where Listed:


Population detail:

Population location: entire
Listing status: E

For most current information and documents related to the conservation status and management of Bettongia lesueur , see its USFWS Species Profile

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Status

Classified as Near Threatened (NT) on the IUCN Red List (1) and listed on Appendix I of CITES (3).
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Population

Population
It is abundant on Barrow (total 3,400 individuals), Bernier (total of 650 individuals), and Dorre (1,000 individuals). These populations appear to be stable (Richards 2005). The populations on Bernier and Dorre Islands (and presumably Barrow Island and possibly mainland populations) are known to undergo extreme fluctuations in response to rainfall and drought (Short et al. 1997).

Estimates for the reintroduced island populations are as follows: Boodie (few hundred), Faure Island (150 individuals); it is extinct on Dirk Hartog Island (Burbidge and Short 2008). Reintroduced mainland populations include: Arid Recovery (500), Scotia (300); Heirisson Prong (20). Populations are increasing where reintroduced.

Population Trend
Increasing
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Threats

Threats

Major Threats
The current major threats to the natural populations of the species include: the accidental introduction of predators (introduced cats and foxes), fire, and disease (Richards 2005). Introduced rats and mice are also a concern, but to a lesser degree than introduced predators. These same threats apply to varying degrees to the reintroduced populations. Extreme fluctuations in populations on islands are a threat, but this threat is seen as minor relative to the risk exotic predators being introduced (Short et al. 1997). It is also unclear to what extent population fluctuations occur at the reintroduction sites on the mainland. This species would likely qualify as having "extreme fluctuations" in population in terms of the IUCN criteria (IUCN 2001) if it were still restricted to the islands off of Western Australia. This is because these fluctuations are tied to climatic extremes that are likely to be synchronous in these locations, but unlikely to be in synchrony with fluctuations (should they occur) in reintroduced populations in South Australia and New South Wales.

Presumably, overgrazing of suitable habitat by cattle and rabbits, loss of wooded areas to agriculture, as well as changes to the fire regime contributed to the decline of the species on mainland Australia. Introduced species, particularly feral cats and foxes, are thought also to have led to its mainland demise (Richards 2005). Feral cats are a proven threat to this species, as they predated on all animals in a trial reintroduction in the Gibson Desert, Western Australia (A. Burbidge pers. comm.). It is believed to have been extirpated from Dirk Hartog Island by foxes and/or feral cats (Burbidge and Short 2008). The role of disease unclear, but may have been a historical threat.

Black rats were a historical threat to the species on Boodie Island. It suffered greater losses, however, due to a rat-baiting program that accidentally eradicated the species from island in 1985. In 1993 the species was reintroduced to Boodie Island from Barrow Island (Morris 2002).
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Threats

This Australian species has been completely lost from the mainland, though in 1855-56 they were reported as being abundant. They were considered as agricultural pests by farmers who settled in Australia in the 19th century, and were shot and poisoned in their hundreds (2). Introduced feral animals such as foxes are thought to have kept their numbers low, as has competition from other introduced species such as rabbits, cattle and black rats (Rattus rattus) (4). Increased grazing and changes to fire regimes have also significantly reduced vegetation cover for this species (5).
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Management

Conservation Actions

Conservation Actions
This species is listed as a threatened species under Australian law. Bernier, Dorre, and Barrow Islands are all protected areas, as are all the areas where the species has been reintroduced. Studies are underway into the taxonomic identity of remaining populations. There is a need to actively manage and monitor populations. This species is listed on Appendix I of CITES.

A recovery plan for the species has been developed for the 2005-2010 period (Richards 2005). Recommendations in this plan include: protect wild populations and their habitat so that the species does not fall below the level of natural fluctuations; maintain captive populations (currently there are captive breeding populations at Yookamurra Wildlife Sanctuary, Scotia Wildlife Sanctuary, and Return to Dryandra Field Breeding Facility); use of population viability analysis to compare the viability of wild, current and potential reintroduced populations, and; enhance community participation and education.

The recovery plan also recommends initiating three reintroductions to the mainland within a five year period (2005-2010) (Richards 2005). There have been reintroduction attempts in the past. Many of these failed do to the presence of introduced predators, and it is clear that success of reintroductions requires sites to be free from cats and foxes. There is a proposed reintroduction to Dirk Hartog Island, which is not possible unless feral cats there have been eradicated (A. Burbidge pers. comm.).
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Conservation

The four islands on which this species occurs have been declared as nature reserves (5). Dirk Hartog Island and the Gibson Desert Nature reserve have also been recommended as sites for translocation of populations following the success on Faure island (5) (7). In addition, research is underway to identify the causes of this species' decline so that conservation practices are well informed (5). The Western Australian Department of Conservation and Land Management (CALM) is responsible for the conservation of this species and it is hoped that these new efforts will enable this unique species to recover (5).
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Relevance to Humans and Ecosystems

Benefits

Economic Importance for Humans: Negative

Burrowing bettong are often thought of as a pest species in areas where crops are present. Humans have hunted them to reduce their impact on crops and are one of the causes for population declines.

Negative Impacts: crop pest

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Economic Importance for Humans: Positive

Burrowing bettongs may be an ecotourism draw because of their rarity.

Positive Impacts: ecotourism

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Wikipedia

Boodie

The boodie (Bettongia lesueur), also known as the burrowing bettong, is a small marsupial. It is a fascinating example of the effects of introduced animals on Australian fauna and ecosystems. Once the most common macropodiform mammal on the whole continent, the boodie now only lives on off-lying islands and in a newly introduced population on the mainland at Shark Bay.[3] This animal, first collected during an 1817 French expedition of the west coast, was named after Charles Lesueur, an artist and naturalist who accompanied a previous French expedition. B. lesueur is known by many common names, including the tungoo, Lesueur’s rat-kangaroo, and the short-nosed rat-kangaroo.[4]

Contents

Taxonomy

The boodie belongs to the family Potoroidae, which includes the rat-kangaroos, potoroos, and other bettongs. Four species make up the genus Bettongia. Also, three subspecies of the boodie exist: Bettongia lesueur graii, the extinct mainland subspecies; Bettongia lesueur nova, an undescribed species on Barrow and Brodie Island; and Bettongia lesueur lesueur.[5]

Paleontology

In the late Oligocene, fossils of paleopotoroines and potoroines (potoroid ancestors) appear. During the Oligocene, ice buildup on Antarctica resulted in less rainfall on Australia. Rainforests declined, replaced by more arid-tolerant leathery leaf woodlands and reed swamps. This climate shift may have favored a radiation of terrestrial marsupials, including potoroid ancestors.[6] Fossils of the Potoroidae family appear from the mid-Miocene to Recent sediments.[7] Subfossil records of the burrowing bettong have been found in West Victoria, western New South Wales, and South Australia.[8]

Morphology

The boodie is a small, rat-like marsupial with short, rounded ears and a lightly haired, thick tail. This animal has a pointed rostrum and beady black eyes, hind limbs longer than the forelimbs and large hind feet. This bettong is yellow-gray above and light gray below. Its short, dense fur feels soft and woolly. The animal bears a faint hip stripe and a distinctive white tail tip. This tail is weakly prehensile and used to carry nest material.[8][9] About the size of a wild rabbit, this little marsupial weighs an average of 1.5 kg.[4] Head and body length is an average of 40 cm.[8] Little to no sexual dimorphism seems to exist. However, morphology varies among subspecies and between islands.[10]

In general, a potoroid skull can be separated from a macropodid skull by the presence of well-developed upper canines and large plagiaulacoid (bladelike) premolars. Also unlike macropodids, the squamosal bone widely contacts the frontal. B. lesueur skulls are short and broad with large palatal vacuities, inflated auditory bullae, and short, broad nasals. The mandible is relatively short and deep compared to other relatives. The dental formula for all the modern potoroines is I 3/1 C 1/0 PM 1/1 M 4/4. Molars are bunodont and quadrate, and the premolars have 9-11 fine, vertical ridges. Young bettongs have two molars which are replaced by one adult premolar; this event is a good indication of maturity. The post-cranial skeleton of all potoroids has 7 cervical, 13 thoracic, 6 lumbar, 2 sacral, and 22 caudal vertebrae, with 13 pairs of ribs.[7]

Reproduction

If conditions are good, the Boodie seems to mate throughout the year, probably utilizing a polygynous mating system. Males do not seem to have dominance hierarchies; rather, they defend females against other males. Some females seem to establish associations with other females; whether these contribute to increased reproductive success is unknown.[7][3] Gestation lasts 21 days, with only one young per litter. Like other marsupial newborns, the newborn is altricial. About four months elapse until weaning.[4] After young leave the pouch, they take 6-7 months to sexually mature.[10] Females mate the day after giving birth, and the fertilized egg arrests development until the young is weaned. This is an example of facultative embryonic diapause. In captivity, females are able to bear three young per year.[4]

Ecology

The boodie once lived in a range of dry subtropical and tropical habitats, from open eucalyptus and acacia woodlands to arid spinifex grasslands. In its current range on the islands, it seems to prefer open Triodia (spinifex) and dune habitats, but will burrow anywhere except places with rocky substrate.[10] The burrowing bettong eats a variety of food, such as seeds, fruits, flowers, tubers, roots, succulent leaves, grasses, fungi, termites, and marine refuse. It will also raid vegetable gardens. Current populations fluctuate, building up during the years with average or good rainfall and crashing during drought years.[4][5] These marsupials are known to live at least three years in the wild.[10]

After colonization of Australia, predators were mainly the introduced red fox and cats.[4] Some natural predators on the islands include the wedge-tailed eagle and sea eagles; on Barrow Island, monitor lizards appear to be a significant predator.[10] Before its extinction on the mainland, the boodie served a very important function in the Australian grassland ecosystem. As it foraged, it mixed organic matter into the soil, spreading fungi and seeds. This mixing also increased water absorption into the soil and reduced the combustible material under trees, decreasing the likelihood of fire. These actions helped maintain the balance of trees, shrubs, and grasses. The loss of small, ground foraging animals after European settlement contributed to widespread soil deterioration.[11] Also, B. lesueur may have helped to thin woody weeds on rangeland by browsing shrubs growing after fires.[12]

Behavior and physiological attributes

B. lesueur is very vocal, communicating through grunts, hisses, and squeals.[8] It shelters in underground burrows, the only macropodiform to do so.[3] Burrows vary from simple tunnels to complex networks with multiple entrances and deep, interconnecting tunnels. These elaborate burrows, or warrens, have been seen having from 4 to 94 entrances.[8] Warrens are communal, housing an average of 20-40 bettongs. Bettongs appear to switch warrens from time to time, though each has one or two preferred warrens. During the day in the warrens, they form groups of one male and one or many females; males never share warrens with other males. Some of the female-female groups seem to be mother-daughter associations. However, individuals seem to forage alone, showing none of the day-range group associations.[3][10]

The boodie is nocturnal, sheltering during the day in burrows and foraging widely at night for food.[4] Locomotion is mainly with the hind legs. The forelimbs are used for support when the boodie is stationary.[8] This bettong exhibits a slow gait and fast gait. The fast gait (or bipedal hop) is characteristic of the macropodiforms and uses only the hind limbs, with the forelimbs held close to the body and tail acting as a counter-balance. The slow gait (or quadrupedal crawl) is used during foraging and other unstressed times.[7] Nighttime movement is usually fairly limited, averaging less than 200 m. However, researchers have measured this marsupial traveling 2.2 km searching for food. One individual tracked on Barrow Island traveled 5 km.[10] B. lesueur uses scent to locate food, which it digs up with the claws on its strong forelimbs.[5] The boodie will even climb into low shrubs to find food.[4] Demonstrating little interspecific interactions, bettongs are apparently undisturbed by run-ins with other non-predators.

Bettong digestive systems are characterized by a very large sacciform forestomach, a tubiform forestomach with limited sacculation, and a small hind stomach. The hind gut has a well-developed, simple cecum. Like many macropodiforms, bettongs have foregut fermentation. Daily water intake is only about 3% of its body weight. B. lesueur seems to have renal adaptations to conserve water, which is important in its arid and semi-arid habitats.[7]

Conservation

Researchers have proposed many possible causes for the boodie's decline on mainland Australia, which began once Australia was colonized. Nineteenth century colonists killed boodies, considering them a destructive garden pest. As ranches spread over the grasslands, livestock grazing reduced vegetation cover, shrinking the rat-kangaroo's habitat. Also, introduced species such as foxes, cats, and rabbits took a severe toll on the boodie, especially on islands. Rabbits competed with them for food and shelter, and the foxes and cats became their major predators. The theory that rabbits compete with boodies for food has been disputed in a study done in 2002 [13] although further investigation is needed. Finally, the Aboriginals maintained certain fire regimes, and when these ceased, the habitat probably changed.[4] By the 1960s, all the boodies on the mainland were extinct.[5]

Once present in all mainland states except Queensland, the boodie survived on three remnant populations on small offshore islands. These islands include Bernier and Dorre Islands in Shark Bay and Barrow Island off the northwest coast of Western Australia. The marsupial was listed on the 2006 IUCN Red List as Vulnerable due to acute restriction of its area of occupancy to less than 100 km². In 2008 however, due to successful conservation efforts both by government agencies and the private sector, boodies have been listed on the 2008 IUCN Red List as Near Threatened, as its range and population have increased, and are still increasing. Newly established populations included Herrison Prong on mainland Shark Bay by the DEC, as well as Faure Island, Scotia Sanctuary, and also Yookamurra Sanctuary, which were etsablished by the Australian Wildlife Conservancy.

References

  1. ^ Groves, C. (2005). Wilson, D. E.; Reeder, D. M. eds. Mammal Species of the World (3rd ed.). Baltimore: Johns Hopkins University Press. pp. 57. OCLC 62265494. ISBN 0-801-88221-4. http://www.bucknell.edu/msw3. 
  2. ^ Richards, J., Morris, K. & Burbidge, A. (2008). Bettongia lesueur. In: IUCN 2008. IUCN Red List of Threatened Species. Downloaded on 29 December 2008. Database entry includes justification for why this species is listed as near threatened
  3. ^ a b c d Sander, U., Short, J., & Turner, B. (1997). "Social organisation and warren use of the burrowing bettong Bettongia lesueur (Macropodoidea: Potoroidae)". Wildlife Research 24 (2): 143–157. doi:10.1071/WR96021. 
  4. ^ a b c d e f g h i "The burrowing bettong (Bettongia lesueur)". Heirisson Prong Threatened Species Project. 2005-09-25. http://www.wildliferesearchmanagement.com.au/bettong.htm. Retrieved 2006-12-08. 
  5. ^ a b c d Massicot, P. (2006-06-02). "Burrowing Bettong". Animal Info. http://www.animalinfo.org/species/bettlesu.htm. Retrieved 2006-12-08. 
  6. ^ Burk, A. & Springer, M.S. (2000). "Intergeneric relationships among Macropodoidea (Metatheria:Diprotodontia) and the chronicle of kangaroo evolution". Journal of Mammalian Evolution 7 (4): 214–237. doi:10.1023/A:1009488431055. 
  7. ^ a b c d e Seebeck, J.H. and Rose, R.W. (1989). "Potoroidae". In eds. D.W. Walton and B.J. Richardson. Fauna of Australia. Vol 1B Mammalia. Australian Government Publishing Service. http://www.deh.gov.au/biodiversity/abrs/publications/fauna-of-australia/pubs/volume1b/30-ind.pdf. 
  8. ^ a b c d e f Burrowing bettong (boodie). Nature Base Fauna Species Profiles.
  9. ^ Burrowing bettong (Bettongia lesueur). (2006). ARKive.
  10. ^ a b c d e f g Short, J. & Turner, B. (1999). "Ecology of burrowing bettongs, Bettongia lesueur (Marsupialia: Potoroidae), on Dorre and Bernier Islands, Western Australia". Wildlife Research 26 (5): 651–669. doi:10.1071/WR98039. 
  11. ^ Martin, G. (2003). "The roll of small ground-foraging mammals in topsoil health and biodiversity: Implications to management and restoration". Ecological Management & Restoration 4 (2): 114–119. doi:10.1046/j.1442-8903.2003.00145.x. 
  12. ^ Sarre, A. (1999). "Slow change on the range". Ecos (100): 44. doi:10.1071/EC100p44. http://www.publish.csiro.au/?act=view_file&file_id=EC100p44.pdf. 
  13. ^ ROBLEY, A. J., SHORT, J. & BRADLEY, S. (2002) Do European rabbits (Oryctolagus cuniculus) influence the population ecology of the burrowing bettong (Bettongia lesueur)? Wildlife research, 29, 423-429.

Tim Flannery (2007). Chasing Kangaroos: A Continent, a Scientist, and a Search for the World's Most Extraordinary Creature, ISBN 978-0-8021-1852-3

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