Overview

Brief Summary

Biology

Living in small colonies that occupy a suitable patch of rocky habitat, both male and female brush-tailed rock wallabies establish territories, which are vigorously defended. Each adult male territory may overlap with the territory of one or more adult females (2). Males are thought to have more than one female partner at a time, while females mate with only a single male, until he disappears from the colony and will then mate with another male. Female brush-tailed rock wallabies give birth to a single young, known as a joey, at a time, after a gestation period of approximately 30 days (2). With undeveloped eyes, hindlimbs and tail, the tiny joey immediately climbs up its mother's fur into her pouch (4), where it will remain for the first six months of life (2). Following this period, 7 to 20 days are spent moving in and out of the pouch, and by the age of nine months, the joey is fully weaned. In the wild, brush-tailed rock wallabies have a life span of five to ten years (2). The brush-tailed rock wallaby is most active during dusk and dawn, during which times it will move across rocks, scramble up cliff faces, and leap over leaning tree trunks with remarkable ease (3), as it travels to areas where it can feed on a variety of grasses and shrubs (2). During the drier, hotter summer months of Australia, this rock wallaby feeds on the juicy bark and roots of various trees, which provide sufficient moisture to allow the rock wallaby to exist for long periods without water (3). During the less active periods of the day, the brush-tailed rock wallaby can be found resting under the shelter of a cave, overhang or vegetation, or sunning themselves on steep rocks. These shelters also proved refuge from predators, such as foxes, dogs, cats, wedge-tailed eagles, (Aquilla audax) and possibly tiger quolls (Dasyuridae) (2).
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Comprehensive Description

Description

This agile marsupial has many adaptations to allow it to move swiftly through rugged habitat (2). The flexible, well-padded hindfeet have roughly textured soles, giving secure grip on rocks, and the long, bushy tail provides balance as they leap over boulders (2) (3). Their long, dense fur is typically dull brown above, reddish-brown on the rump, and lighter on the underparts. The flanks bear distinct pale grey and black stripes (2). As its name suggests, the end third of this rock wallaby's tail is bushy, and is generally brown to black (2). Like other wallabies, female brush-tailed rock wallabies have a forward-opening pouch, in which the newborn infants develop, and four mammae (3),
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Distribution

Range Description

The Brush-tailed Rock Wallaby is endemic to south-eastern Australia, where it occurs in south-eastern Queensland, eastern New South Wales, and as a tiny population in the East Gippsland of eastern Victoria.
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Geographic Range

Native to Australia, brush-tailed rock-wallabies are distributed along rocky escarpments of the Great Dividing Range from southern Queensland to western Victoria. Although common in south-eastern Queensland and northern New South Wales, populations in the southern and western parts of the range have declined. Remnant populations in Victoria and western New South Wales are endangered. Only three colonies in south-eastern Australia remain, and estimates of the total wild population in this region are at fewer than 12 individuals.

Petrogale penicillata was introduced to Hawaii and New Zealand. In Hawaii, a small population of rock-wallabies, descended from two animals, has existed on the island of Oahu since 1916. In New Zealand, brush-tailed rock-wallabies were introduced in the 1870s and can be found on Kawau, Rangitoto, and Montutapu islands. On some of these islands rock-wallabies are regularly culled because they have reached pest proportions.

Biogeographic Regions: australian (Native ); oceanic islands (Introduced )

  • Taggart, D., D. Schultz, C. White, P. Whitehead, G. Underwood, K. Phillips. 2005. Cross-fostering, growth, and reproductive studies in the brush-tailed rock-wallaby, Petrogale penicillata (Marsupialia: Macropodidae): efforts to accelerate breeding in a threatened marsupial species. Australian Journal of Zoology, 53: 313-323.
  • Eldridge, M., R. Close. 1995. Brush-tailed rock-wallaby. Pp. 383-385 in R Strahan, ed. The Mammals of Australia. Chatswood, NSW: Reed Books.
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occurs (regularly, as a native taxon) in multiple nations

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National Distribution

United States

Origin: Exotic

Regularity: Regularly occurring

Currently: Present

Confidence: Confident

Type of Residency: Year-round

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Global Range: Native to mountainous regions of eastern New South Wales, Australia, where now scarce (Tomich 1986); suitable areas throughout Australia, including many nearby islands, but not Tasmania (Nowak 1991:96). Introduced (1916) in Hawaii (leeward Oahu; population apparently concentrated on northwestern side of Kalihi Valley) (Tomich 1986).

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Range

The brush-tailed rock wallaby is endemic to Australia, where it occurs in small, isolated populations dotted across south-eastern Queensland, eastern New South Wales and Victoria (3).
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Physical Description

Morphology

Physical Description

Petrogale penicillata has a dull-brown back, paler chest and belly, a rufous rump and black, furry feet. They have a black axillary patch often extending as a dark stripe to the margin of the hindlegs. Their tail darkens distally with a prominent brush. Their pelage is long and thick, especially about the rump, flanks and base of tail. Animals from the northern part of the range tend to be lighter and have a less prominent tail brush. They have long tails, slightly longer than their head and body length. Head and body length averages 55.7 cm in males and 53.6 cm in females, while tail length averages 61.1 cm in males and 56.3 cm in females.

Range mass: 4.0 to 10.9 kg.

Range length: 45 to 58.6 cm.

Other Physical Features: endothermic ; homoiothermic; bilateral symmetry

Sexual Dimorphism: male larger

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Ecology

Habitat

Habitat and Ecology

Habitat and Ecology
Brush-tailed Rock Wallabies are found in structurally complex, rocky habitats. Often these areas are gorges, cliffs, rock outcrops, or boulder piles. Most of these sites have a northerly aspect, but this appears not to be as important as rock complexity that contains a number of refuges from predators (Murray et al. 2008). The rocky environments occur within a variety of vegetated landscapes from dense rainforest to dry sclerophyll or open woodland (Eldridge and Close 2008). This species occurs as small colonies, usually with less than 30 individuals, but sometimes more (Piggott et al. 2006). These colonies run the risk of becoming inbred. Highly structured breeding and male dispersal have helped reduce the risk of inbreeding (Hazlitt et al. 2004), but as these colonies become increasingly isolated they are at greater risk (Hazlitt et al. 2006a,b).

Systems
  • Terrestrial
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Habitat

Brush-tailed rock-wallabies live on rock faces close to grassy areas and often in open forests. They prefer sites with numerous ledges, caves, and crevices. They typically occupy sites with a northerly aspect, in order to sun themselves in the morning and the evening. Originally widespread and abundant, brush-tailed rock-wallabies were found in suitable rocky areas in a wide variety of habitats, including rainforest gullies, wet and dry sclerophyll forest, open woodland, and rocky outcrops in semi-arid country.

Habitat Regions: temperate ; tropical ; terrestrial

Terrestrial Biomes: savanna or grassland ; forest ; rainforest ; scrub forest

Other Habitat Features: caves

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Comments: Rocky ranges and boulder-strewn outcrops with an associated cover of forest, woodland, heath, or grassland; agile among rocks, moves awkwardly in the open (Nowak 1991). Rocky cliff faces, steep open slopes, dry ledge and cave habitat with southern exposure.

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Habitat

In accordance with its name, this wallaby inhabits rocky areas and boulder strewn outcrops, where nearby forest, woodland, heath or grassland provide important cover (3).
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Migration

Non-Migrant: Yes. At least some populations of this species do not make significant seasonal migrations. Juvenile dispersal is not considered a migration.

Locally Migrant: No. No populations of this species make local extended movements (generally less than 200 km) at particular times of the year (e.g., to breeding or wintering grounds, to hibernation sites).

Locally Migrant: No. No populations of this species make annual migrations of over 200 km.

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Trophic Strategy

Food Habits

Petrogale penicillata feeds largely on grasses, which comprise 35-50% of its total diet, but will supplement its diet with leaves, sedges, ferns, roots, bark, fruit, seeds and flowers. Brush-tailed rock-wallabies choose to forage in locations with more forbs and short green grasses. There is little seasonality of diet. Also, the relative proportions of different food types in the diet are vary little among regions, despite varying vegetation. This sugests definite food preference with little or no seasonal shortages of preferred foods. Since brush-tailed rock-wallabies eat a wide range of food items, they are likely buffered against drought and against competition with more specialized herbivores.

Plant Foods: leaves; roots and tubers; wood, bark, or stems; seeds, grains, and nuts; fruit

Primary Diet: herbivore (Folivore )

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Comments: Diet consists mainly of grasses; also eats juicy bark and roots of various trees (Nowak 1991). Diet in Hawaii mainly grasses and Osteomeles (Kramer 1971).

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Associations

Ecosystem Roles

When they were more widespread, brush-tailed rock-wallabies substantially affected agricultural plant species. In 1880, legislation was passed in New South Wales declaring kangaroos and wallabies as vermin. A bounty was offered on brush-tailed rock-wallabies, suggesting that they threatened agricultural production. They apparently invaded orchards and vegetable gardens with their ability to jump on top of fences, and fed heavily on the plants there. Additionally, it is possible that brush-tailed rock-wallabies help disperse the seeds of the fruit they eat. For instance, large numbers of the seeds of Persoonia linearis were found in the wallabies' faecal pellets collected in the spring.

Ecosystem Impact: disperses seeds

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Predation

Since brush-tailed rock-wallabies exhibit very high fidelity to diurnally used sites, predators may find it easy to learn where to find them. Furthermore, because colonies are small (due to declining population size), fewer individuals are available to be alert in order to detect and warn of approaching predators. Since Petrogale penicillata has been observed to maintain a relatively constant level of vigilance regardless of surrounding vegetation, however, it has been suggested that these animals rely on early detection of predators. Additionally, brush-tailed rock-wallabies are much more agile than their predators.

Known Predators:

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General Ecology

Reportedly lives in small groups that have a defended territory; males have a linear dominance hierarchy (Nowak 1991).

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Life History and Behavior

Behavior

Communication and Perception

Petrogale penicillata engages in allogrooming, where one animal bites and licks the fur of another animal, which may serve a role in reinforcing dominance status. Other examples of communicative behaviors include making vocalizations (a hissing cough sound), staring intensely, and aggressive behaviors such as nose jabbing (one animal thrusting its nose toward another animal). Males may examine potential female mates by approaching the female and sniffing her rump or cloaca.

Additionally, some evidence suggests that adult males deposit scent marks within their area of control.

Communication Channels: visual ; tactile ; acoustic ; chemical

Other Communication Modes: scent marks

Perception Channels: visual ; acoustic

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Cyclicity

Comments: Basically nocturnal; may emerge on warm afternoons to bask in the sun (Nowak 1991).

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Life Expectancy

Lifespan/Longevity

Captive brush-tailed rock-wallabies have lived over 11 years.

Average lifespan

Status: captivity:
11 years.

Average lifespan

Status: captivity:
14.4 years.

  • Lavery, H., T. Kirkpatrick. 1985. Kangeroos as pests. Pp. 103-132 in H Lavery, ed. The Kangeroo Keepers. St. Lucia, Queensland: University of Queensland Press.
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Lifespan, longevity, and ageing

Maximum longevity: 14.3 years (captivity)
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Reproduction

Reproduction

Brush-tailed rock-wallabies breed year round. The few matings that have been observed among Petrogale penicillata involve only females and males who are established on refuges. A notable feature of brush-tailed rock-wallabies, as well as other Petrogale species, is close and regular association between the refuge-guarding male and the females who use his refuge. Association involves mutual grooming and unusually high tolerance of proximity.

Though details are unavailable on brush-tailed rock-wallabies, most species of Macropodidae are promiscuous. Brush-tailed rock-wallabies have a different mating system than most related species in three respects: 1) a higher proportion of adult males are likely to take part in breeding and may do so for many years, 2) variance in male reproductive success is relatively low, and 3) only some weaned females, those able to establish themselves on a refuge, are likely to breed at all.

Mating System: polygynous

Females are sexually mature by 18 months, and males by 20 months. They breed all year, mating soon after giving birth. Development of the embryo is delayed until the pouch is vacated. Pregnancy lasts 31 days, after which a single young is born and attaches to one of the 4 teats in the pouch. The young remains in the pouch for about 29 weeks, then suckles at foot for about three months. In captive animals, post-partum estrous was typically observed on the same day as birth, even sometimes appearing within a few hours.

The process of birth has been observed on one occasion in the rock-wallaby Petrogale penicillata inornata. The female sat on the base of her tail, her body leaning forward in order to bring the head close to the urogenital opening and pouch. Birth was accompanied by a small amount of clear fluid and blood, which the mother cleaned as the newborn young went toward the pouch opening. It took 45 seconds for the infant to reach the pouch opening from the urogenital opening. The mother remained in the birth position for 10 more minutes, licking around the urogenital opening.

Breeding interval: The breeding interval is unknown, but females can enter estrous shortly after giving birth and breed throughout the year.

Breeding season: Brush-tailed rock-wallabies breed throughout the year.

Average number of offspring: 1.

Average gestation period: 31 days.

Average weaning age: 7 months.

Average time to independence: 7 months.

Average age at sexual or reproductive maturity (female): 18 months.

Average age at sexual or reproductive maturity (male): 20 months.

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

Average gestation period: 30 days.

Average number of offspring: 1.

Average age at sexual or reproductive maturity (male)

Sex: male:
590 days.

Average age at sexual or reproductive maturity (female)

Sex: female:
540 days.

There are few details about parental investment in Petrogale penicillata. Young remain in the mother's pouch for around 29 weeks, where they receive protection and milk. After leaving the pouch, the evicted young continue to suckle for about 3 months.

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

  • Jarman, P., P. Bayne. 1997. Behavioural ecology of Petrogale penicillata in relation to conservation. Australian Mammalogy, 19: 219-228.
  • Johnson, P. 1979. Reproduction in the plain rock-wallaby, Petrogale penicillata inornata Gould, in captivity, with age estimation of the pouch young. Australian Wildlife Research, 6: 1-4.
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In Australian captives: gestation 30-32 days; pouch life about 7 months (189-227 days); sexually mature in 18 months (590 days in males, 540 days in females) (Johnson 1979, Nowak 1991). Births have been recorded in March, June August, and September; litter size normally is 1; has lived over 14 years in captivity (see Nowak 1991).

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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
Taggart, D., Menkhorst, P. & Lunney, D.

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

Justification
Listed as Near Threatened because this species is in significant decline (but at a rate of less than 30% over ten years) due to predation by, and competition with, introduced species and by fragmentation that has led to increasingly isolated populations that are prone to extinction, making the species close to qualifying for Vulnerable under criterion A.

History
  • 1996
    Vulnerable
  • 1994
    Vulnerable
    (Groombridge 1994)
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Conservation Status

In many parts of New South Wales, Petrogale penicillata populations have been reduced to small, isolated colonies. Predation, notably by red foxes (Vulpes vulpes), an introduced species to Australia, appears to be the current major threat to Petrogale penicillata. Habitat degradation through vegetation and fire changes, competition with goats, rabbits and sheep, and vulnerability to drought and disease may also be involved. Brush-tailed rock-wallabies have been observed to leave properties where sheep were introduced, suggesting that the habitat-specific rock-wallabies were starved out by the much more ubiquitous sheep.

The observation of the dramatic decline of a wild colony at the Jenolan caves in central New South Wales led to the first concerted management response to the continuing decline of Petrogale penicillata. The colony was of unknown size but supplemented by the release of 88 locally enclosure-bred animals in 1988. Late in 1992, the remaining wild animals at Jenolan were trapped and transferred to a nearby enclosure with the goal of establishing a captive breeding program. Such captive breeding programs generally allow for a far greater degee of direct control than can be exercised with wild animals. The NSW National Parks and Wildlife service (NPWS) has responded to the ongoing decline of Petrogale penicillata by initiating a program incorporating: 1) A survey to locate all sites where Petrogale penicillata> is extant; 2) a community awareness and involvement campaign; 3) the development and implementation of Population Management Plans (PMPs) for extant sites; 4) on-going research into threats and impacts.

US Federal List: no special status

CITES: no special status

IUCN Red List of Threatened Species: near threatened

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National NatureServe Conservation Status

United States

Rounded National Status Rank: NNA - Not Applicable

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NatureServe Conservation Status

Rounded Global Status Rank: G4 - Apparently Secure

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Status

Classified as Near Threatened (NT) on the IUCN Red List (1).
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Population

Population
This species is sparsely distributed within abundant suitable habitat (Eldridge and Close 2008). It is difficult to estimate population sizes because it is nocturnal, and occurs in very rugged terrain. The species is declining at many localities and the overall population is in decline. The total population size is estimated to be between 15,000 and 30,000 individuals (DECC 2008). The stronghold for the species is within north-eastern New South Wales, containing as much as 80% of the total population – most of which is within the Macleay River and Clarence River gorges (DECC 2008). An estimated 2% of the population occurs elsewhere in New South Wales, 17% within Queensland, and less than 1% in Victoria (DECC 2008).

Population Trend
Decreasing
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Threats

Threats

Major Threats
There is a lack of data about the threats to the Brush-tailed Rock Wallaby (Eldridge and Close 2008). Predation by introduced foxes and competition with introduced goats are likely to be the greatest threats. Foxes prey on young rock wallabies and probably limit dispersal as well as recruitment. Introduced dogs and cats are also probably threats, but the habitat in which this species lives is not well suited to these predators. Habitat fragmentation and land clearance between colonies is also thought to limit dispersal and reduce numbers of individuals by exposing rock wallabies to higher rates of predation. As colony isolation increases so does the risk of inbreeding (Hazlitt et al. 2006a,b).

Hunting was perhaps the main factor in reducing the population and range of this species. A sustained commercially-driven period of hunting led to the decline of many populations and local extinctions, and may have been the primary cause of the initial decline, at least in central and southern New South Wales. Bounties were paid on over half a million rock-wallabies between 1894 and 1914 (Short and Milkovits 1990) and there was an extensive fur trade from pre-1890 to 1927 (Lunney et al. 1997). The species was also hunted extensively in the Grampians area of Victoria. The magnitude of hunting is apparent when one considers that the current population of the species is estimated at between 15,000 and 30,000 individuals, and in 1908 alone 92,590 skins were marketed by a single company (Lunney et al. 1997).
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Threats

Once one of the most widespread of the rock wallabies, this bushy-tailed species has been greatly reduced in both numbers and range (3). In the nineteenth and early twentieth centuries, this species was valued for its skin, as well as being thought of as an agricultural pest, and as a result hundreds of thousands were killed (3). Today, numerous threats continue to impact populations, including predation, competition, exotic plant invasion, habitat modification, fire, drought and disease (2). Habitat modification is believed to be one of the most significant threats to this Vulnerable marsupial, with habitat clearance, exotic plant invasion, changed fire regimes, exotic herbivore grazing, and residential and tourist developments, all impacting and altering the brush-tailed wallaby's habitat (2). Predation by introduced red foxes (Vulpes vulpes) is also considered to be one of the major reasons behind these declines, as these agile predators can reach the wallaby's once inaccessible refuges (2).
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Management

Conservation Actions

Conservation Actions
The Brush-tailed Rock Wallaby is listed as a threatened species under Australian law. It occurs within a number of protected areas. A detailed recovery plan has been developed for the species within New South Wales (DECC 2008).

The recovery of this species is particularly complex and requires a consideration of threats and management interventions at a variety of spatial scales – from local to regional (Murray et al. 2008; DECC 2008). Threats also vary across the range of the species so that, for example, fox predation is considered less of a threat in the northern portion of the range than in the south (DECC 2008). Recommendations from the recovery plan (DECC 2008), include: further surveys to improve knowledge of the distribution and abundance of the species; identifying the main local and widespread threats and the interactions between these; monitoring the effectiveness of management responses; expanding existing predator and introduced herbivore control; maintaining and enhancing captive breeding programs for identified regional populations; and continuing and expanding community-based conservation programs.
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Conservation

Conservation of the brush-tailed rock wallaby has, to date, largely taken the form of red fox control programs. Fox control programmes are currently being undertaken in a number of areas, including Warrumbungles National Park, Yengo National Park and Goulburn River National Park (2). However, in 2008, the New South Wales National Parks and Wildlife Service published a recovery plan, which outlines further measures which are to be carried out with the aim of halting the decline in this species, and improving its threatened status. These actions include continuing existing and introducing new predator and introduced herbivore control programs, and continuing and expanding community-based conservation programs. Furthermore, captive populations of the brush-tailed rock wallaby in Australia have allowed important research to be carried out (2).
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Relevance to Humans and Ecosystems

Benefits

Economic Importance for Humans: Negative

When brush-tailed rock-wallabies were more widespread in Australia, they were shot as agricultural pests. They were able to enter and feed in orchards, and vegetable gardens required fences several meters high to exclude them.

Negative Impacts: crop pest

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Economic Importance for Humans: Positive

Captive populations of Petrogale penicillata are the focus of behavioral, management and genetic research.

Positive Impacts: research and education

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Wikipedia

Brush-tailed rock-wallaby

The brush-tailed rock-wallaby or small-eared rock-wallaby (Petrogale penicillata) is a kind of wallaby, one of several rock-wallabies in the genus Petrogale. It inhabits rock piles and cliff lines along the Great Dividing Range from about 100 km north-west of Brisbane to northern Victoria, in vegetation ranging from rainforest to dry sclerophyl forests. Populations have declined seriously in the south and west of its range, but it remains locally common in northern New South Wales and southern Queensland.[3]

External introductions

As part of the acclimatisation movement of the late 1800s, governor Grey introduced this and four other species of wallabies (including the rare parma wallaby) to islands in Hauraki Gulf, near Auckland, New Zealand, where they became well-established. In modern times, these populations have come to be viewed as exotic pests, with severe impacts on the indigenous flora and fauna. As a result, eradication is being undertaken, after initial protection for review of their Australian populations and the return of some wallabies to Australia. Between 1967 and 1975, 210 rock-wallabies were captured on Kawau Island and returned to Australia, along with thousands of other wallabies.[4] Rock-wallabies were removed from Rangitoto and Motutapu Islands during the 1990s, and eradication is now underway on Kawau. Another thirty-three rock-wallabies were captured on Kawau during the 2000s, and returned to Australia, before eradication began.[5][6]

In 2003 some Kawau brush-tails were relocated to the Waterfall Springs Conservation Park north of Sydney, New South Wales, for captive breeding purposes.

Due to an escape of a pair in the 1916, a small breeding population of the brush-tailed rock-wallabies also exists on the island of Oahu in Hawaii.

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. 68. OCLC 62265494. ISBN 0-801-88221-4. http://www.bucknell.edu/msw3. 
  2. ^ Taggart, D., Menkhorst, P. & Lunney, D. (2008). Petrogale penicillata. 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 Field Guide to the Mammals of Australia, Menkhorst, P and Knight, F, Oxford University Press, Melbourne, 2001 ISBN 0-19-550870-X
  4. ^ Shaw, W.B.; Pierce, R.J. 2002: Management of North Island weka and wallabies on Kawau Island. Department of Conservation Science Internal Series 54. Department of Conservation, Wellington. ISBN 0-478-22272-6.
  5. ^ "Rock wallabies". Catalyst (ABC). 4 March 2004. http://www.abc.net.au/catalyst/stories/s1058764.htm. Retrieved 2 March 2012. 
  6. ^ "Saving the Brush-tailed Rock Wallaby". Waterfall Springs Wildlife Sanctuary. http://www.waterfallsprings.com.au/pages/foundation-story.php. Retrieved 2 March 2012. 
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Names and Taxonomy

Taxonomy

Comments: Subspecies purpureicollis and godmani formerly were regarded as distinct species (see Nowak 1991:97).

Individuals on Oahu reportedly do not resemble living Australian individuals or museum specimens--rapid evolution? (Conant 1988). However, genetic data indicate that the Petrogale in Hawaii represent typical P. penicillata and are not consistent with suggestions that the Hawaiian population represents a novel taxon (Eldridge and Browning 2002).

Peradorcas concinna sometimes has been included in the genus Petrogale.

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