Animal Info - Brush-tailed Bettong
(Other Names: Bettong, Bettongie à Queue Touffue, Brush-tailed
Rat Kangaroo, Canguro-rata Colipeludo, Kangourou-rat à Queue Touffue, Woylie)
Bettongia penicillata
Status: Lower
Risk - Conservation Dependent
Contents
1. Profile (Picture)
2. Tidbits
3. Status and Trends (IUCN Status, Countries Where Currently Found, History of
Distribution, Threats and Reasons for Decline)
4. Data on Biology and Ecology (Weight, Habitat, Age to Maturity, Gestation
Period, Birth Season, Birth Rate, Early Development, Maximum Age, Diet, Social Organization, Density and Range)
5. References
Profile
Pictures: Brush-tailed
Bettong #1 (30 Kb JPEG) (Milamba
Aust.); Brush-tailed
Bettong #2 (101 Kb JPEG) (Mus.
Vict.)
The brush-tailed bettong is a marsupial
that once inhabited more than 60% of the Australian
mainland but now occurs only on less than 1%. It is strictly nocturnal and is not gregarious.
During the day it rests in a well-made and hidden nest which consists of grass and
shredded bark. It digs out food such as bulbs, tubers and fungi with its strong foreclaws.
Its habitat includes temperate forests and scrubs as well as arid shrublands and
grasslands.
The brush-tailed bettong formerly ranged over all of southwest Western Australia, most of South
Australia, the northwest corner of Victoria and across the central portion of New South
Wales. It was abundant in the mid-19th century. By the 1920's it was extinct over much of
its range. As of 1992 it was reported only from four small areas of Western Australia. In
South Australia, a number of populations had been established through introduction of
captive-bred animals. As of 1996 it occurred in six sites in Western Australia and on
three islands and two mainland sites in South Australia, following the reintroduction
program and the controlling of foxes.
Its decline seems to have been caused by a number of factors. These include the
impact of introduced grazing animals, clearing for agriculture, fox predation, and
possibly changed fire regimes.
Tidbits
*** The brush-tailed bettong has an unusual diet for a mammal. Although it may eat
bulbs, tubers, seeds, insects and resin, the bulk of its nutrients are derived from
underground fungi, which can only be digested indirectly. In a portion of its stomach, the
fungi are consumed by bacteria. These bacteria produce the nutrients that are digested in
the rest of the stomach and small intestine.
*** It is able to use its tail, curled around in a prehensile
manner, to carry bundles of nesting material.
Status and Trends
- 1960's: Insufficiently Known
- 1980's - 1994: Endangered
- 1996 - 2004: Lower Risk - conservation
dependent (IUCN
2004)
Countries Where the Brush-tailed Bettong Is Currently Found:
2004: Occurs in Australia (IUCN
2004).
History of Distribution:
The brush-tailed bettong formerly ranged from Shark Bay in Western Australia south
and east, covering all of southwest Western Australia, most of South Australia except the
far southeast and northeast portions of the state, the northwest corner of Victoria and
across the central portion of New South Wales, almost to the Queensland border. Also the
Great Sandy, Tanami, Gibson, and Great Victoria Deserts. It was abundant in the mid-19th
century. By the 1920's it was extinct over much of its range. As of 1966 it occurred only
in southwestern Australia, and was considered
probably to be secure at the time. By the late 1980's it was reported only from three
small areas of Western Australia: the Perup and Dryandra Forests and the Tuttanning
Reserve. As of 1992 it occurred in these three areas and also in the State Forest north of
Collie in Western Australia. In South Australia, a number of populations had been
established through introduction of captive-bred animals. As of 1996 it occurred in six
sites in Western Australia and on three islands and two mainland sites in South Australia,
following the reintroduction program and the controlling of foxes.
Threats and Reasons for Decline:
Its decline seems to have been caused by a number of factors. These include the impact
of introduced grazing animals, clearing for agriculture, fox predation, and possibly
changed fire regimes.
Data on Biology and Ecology
The brush-tailed bettong weighs 1.1 - 1.6 kg (2.4 - 3.5 lb).
Habitat:
In South Australia - currently semi-arid
scrublands and grasslands. Western Australia - open eucalypt forest with an understory of
tussock grass, low woody scrub and occasional bare patches of ground in medium rainfall
areas. Formerly its habitat included temperate forests and scrubs and also arid shrublands
and grasslands. It appears to be particularly adapted to habitats that are subject to
frequent fires.
The brush-tailed bettong lives in the Southwest
Australia Biodiversity
Hotspot (Cons.
Intl. 2005).
Age to Maturity:
Females can produce young when only 6 months old.
Undelayed gestation is about 21 days. (But see Birth Rate
below.)
Birth Season:
It breeds throughout the year.
Birth Rate:
In common with many other kangaroos, the brush-tailed bettong mates shortly after
giving birth and can keep embryos in embryonic
diapause until they are needed. A single young spends 90 days in the pouch. There is
an interval of about 100 days between each birth.
Early Development:
A single young spends 90 days in the pouch. The weaned young share the nest and
accompany the mother until they are displaced when a new infant leaves the pouch.
Maximum Age:
8 years and 9 months (in captivity).
Diet:
The brush-tailed bettong does not consume either green material or water. Indeed,
while it may eat bulbs, tubers, seeds, insects and resin, the bulk of its nutrients are
derived from underground fungi, which can only be digested indirectly. In a portion of its
stomach, the fungi are consumed by bacteria. These bacteria produce the nutrients that are
digested in the rest of the stomach and small intestine.
Social Organization:
The brush-tailed bettong is not gregarious.
Density and Range:
The brush-tailed bettong has a home range
averaging 23 hectares (58 acres) for females and 35 hectares (88 acres) for males.
References
Burbidge & McKenzie 1989, Burton & Pearson 1987, Cons.
Intl. 2005, Curry-Lindahl
1972, Earth Sanct., Flannery 1990, IUCN 1968, IUCN 1994, IUCN 1996, IUCN 2000,
IUCN 2003a, IUCN
2004, Kennedy 1992, Milamba
Aust., Mus. Vict.,
Nowak
& Paradiso 1983, Oryx 1980, Oryx 1997b
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