Overview

Distribution

Range Description

This species is endemic to Australia. Its current range is discontinuous with geographically disjunct colonies distributed across northern tropical and subtropical coastal and inland regions (J. Worthington-Wilmer pers. comm.). There are scattered historical records through arid Western Australia, southern Northern Territory, northern South Australia, and western and south-western Queensland.
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Geographic Range

Macroderma gigas or the Ghost Bat is found in Northern Australia where it has a scattered distribution. It is found north of 29°S in Western Australia, Northern Territories, and Queensland.

(Ride 1970, Strahan 1983)

Biogeographic Regions: australian (Native )

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Physical Description

Morphology

Physical Description

SIZE: Head and body length is 10 to 13cm and forearm length is 10.2 to 11.2cm. Females are smaller than males.

WEIGHT: 130 to 170 grams.

Ghost Bats have a light grey, almost white, appearance and large long ears that are joined at the base. The head and body measure up to 130 mm with a wingspan of about 500 mm.

In the Pilbara district of Western Australia, Ghost Bats are of the pale 'ghostly' desert form with ashy-grey back and white under-parts. Juveniles are sooty-grey all over. In the northern part of their range, especially in Kimberley, Arnhem Land, and around Rockhampton in Queensland, adult Ghost Bats are a dark sooty-grey.

(Nowak 1991, Ride 1970, Strahan 1983)

Range mass: 130 to 170 g.

Range length: 115 to 130 mm.

Average length: 127.50 mm.

Average wingspan: 500 mm.

Other Physical Features: endothermic ; bilateral symmetry

Average basal metabolic rate: 0.639 W.

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Ecology

Habitat

Habitat and Ecology

Habitat and Ecology
Although it occurs in rainforest areas, the Ghost Bat is mainly found in the arid zone near rock outcrops, and roosts in caves, mines, and rock clefts. The species also occurs throughout the tropical savanna, in savanna woodlands, and in mangroves (N. McKenzie pers. comm.). It generally forages within 1-2 km of the roost site. Most of the prey are large invertebrates such as beetles, but it is also known to take small vertebrates including other bats, birds, lizards, and snakes (Tidemann et al. 1985). In captive feeding experiments some fruit will be eaten only when no animal food is available (Douglas 1967). Most prey is taken to a feeding perch in trees, rock overhangs, or cave entrances (Hutson et al. 2001).

Ghost bats move between a number of caves seasonally or as dictated by weather conditions. Thus they require a range of cave sites (Hutson et al. 2001). Most maternity sites appear to require multiple entranced caves (L. Hall pers. comm.). Maternity colonies are limited within the range of this species, and include mines, especially in the Pilbara. Generation length is probably around four years and recruitment is very low (L. Hall pers. comm.).

Systems
  • Terrestrial
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Habitat

Ghost Bats have been recorded in both arid regions (Pilbara region) and rainforest areas (north Queensland). Macroderma gigas roost in caves, old mine tunnels and in deep cracks in rocks. They usually roost in colonies but, because many of their roosting sites are being destroyed, it is rare to find large colonies. Ghost Bats are distributed widely but patchily across the northern half of Australia and are found in a variety of tropical habitats. Perhaps the species' most famous roosting and nesting sites, and largest colonies, are at Mount Etna caves, near Rockhampton in Queensland.

(Nowak 1991, Ride 1970, Strahan 1983)

Habitat Regions: tropical ; terrestrial

Terrestrial Biomes: forest ; rainforest ; scrub forest

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Trophic Strategy

Food Habits

Macroderma gigas is Australia's only carnivorous bat, eating large insects, reptiles, frogs, birds, small mammals, and sometimes other bat species. Much of this prey is captured on the ground. Ghost Bats drop on mammals from above, enveloping them with their flight membranes, and kill them with bites about the head and neck. They eat large amounts of food including flesh, bones, teeth, fur, small feathers, and the chitinous exoskeletons of insects. Ghost Bats appear to need this roughage in their diet because if they are fed on boneless meat in captivity they soon become distressed and fouled with loose excreta.

(Ride 1970)

Animal Foods: birds; mammals; amphibians; reptiles; insects

Primary Diet: carnivore (Eats terrestrial vertebrates, Insectivore )

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Associations

Ecosystem Roles

Ghost bats are important predators of small mammals, birds, and reptiles in the areas in which they live.

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Predation

Ghost bats have few natural predators, though larger owls may take them at night and young may fall prey to roost predators, such as snakes. Medium-sized owls compete for insects and small mammals.

(Nowak 1991)

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Known prey organisms

Macroderma gigas preys on:
Insecta
Amphibia
Reptilia
Aves
Mammalia

This list may not be complete but is based on published studies.
  • Myers, P., R. Espinosa, C. S. Parr, T. Jones, G. S. Hammond, and T. A. Dewey. 2006. The Animal Diversity Web (online). Accessed February 16, 2011 at http://animaldiversity.org. http://www.animaldiversity.org
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Life History and Behavior

Life Expectancy

Lifespan/Longevity

Information on lifespan in this species is lacking.

Average lifespan

Status: captivity:
22.6 years.

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Lifespan, longevity, and ageing

Maximum longevity: 22.6 years (captivity) Observations: One captive specimen lived for 22.6 years (Richard Weigl 2005).
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Reproduction

Reproduction

Little is known about mating in ghost bats.

Mating takes place in July and August. Gestation lasts about three months and females bear a single young between September and November.  Sexual maturity is attained in the second year of life. (Nowak, 1991, Ride 1970, Strahan 1983)

Breeding season: Mating takes place in July and August, births occur from September to November.

Range number of offspring: 1 (low) .

Average number of offspring: 1.

Average gestation period: 3 months.

Average weaning age: 3 months.

Average age at sexual or reproductive maturity (female): 1 years.

Average age at sexual or reproductive maturity (male): 1 years.

Key Reproductive Features: iteroparous ; seasonal breeding ; gonochoric/gonochoristic/dioecious (sexes separate); sexual ; fertilization (Internal ); viviparous

Average number of offspring: 1.

Mothers form nursery colonies separate from the males while the young are being weaned. While the young are still suckling, they are left in the roost while the females go out to hunt. Juveniles then hunt with their mothers until they become completely independent. Young begin flying at 7 weeks and become weaned by the March following their birth. (Ride 1970, Strahan 1983)

Parental Investment: altricial ; female parental care

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Conservation

Conservation Status

IUCN Red List Assessment


Red List Category
VU
Vulnerable

Red List Criteria
C1

Version
3.1

Year Assessed
2008

Assessor/s
McKenzie, N. & Hall, L.

Reviewer/s
Lamoreux, J. (Global Mammal Assessment Team), Racey, P.A., Medellín, R. & Hutson, A.M. (Chiroptera Red List Authority)

Contributor/s

Justification
Listed as Vulnerable because this species has a small population (less than 10,000 mature individuals), the inferred decline in the last three generations has been greater than 10%, and there is the potential for the population to decline even faster within the next three generations. Populations of the species are fragmented, but not considered to be severely fragmented - other than within the Queensland part of the range - as there is likely to be interchange among colonies within, though not between, other parts of the range.

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

Ghost Bats are sensitive to disturbance. Human intruders to a cave colony may cause the group to become nervous and leave. Many roost caves have been destroyed or are threatened by mining activity. Disturbance and loss of roosting sites due to mining, tourism and internal dereliction of mines through aging of timber supports are known threats. In recent times population declines could be attributable to competition for prey with feral cats, and prey lost through habitat modification by fire and livestock

Ghost Bats are protected by national legislation in Australia.

(UNEP 2001)

US Migratory Bird Act: no special status

US Federal List: no special status

CITES: no special status

IUCN Red List of Threatened Species: vulnerable

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Population

Population
Current total population estimates are between 7,000 and 9,000 individuals, and varies in each of the three range states. The population in Queensland is located in only 4-5 highly disjunct localities and is estimated at less than 1,000 animals, with its major colony at Mount Etna having declined in the last 10 years. The Northern Territory population is thought to be more or less stable at 2,500-3,500 individuals and is distributed among at least 6-7 main population centres, but the largest colony (at Kohinoor Mine, Pine Creek) is potentially threatened by mine collapse. In Western Australia Ghost Bats occur in two separate regions: in the Pilbara, there are c.600 individuals (N. McKenzie pers. comm.), whereas the Kimberley population is inferred to be about 3,000-4,000 individuals (N. McKenzie pers. comm.).

Population Structure:
The species has undergone a major population genetic analysis, with nearly all major known localities included with the exception of the Kimberley, Western Australia and some Northern Territory populations. These studies have shown that Macroderma gigas populations are highly structured, being genetically distinct at both regional and local scales (Worthington-Wilmer et al. 1994, 1999; Armstrong et al. in prep). Populations at the southern limits of the species range are geographically isolated separated by a minimum distance of 300 km. This geographic isolation is reflected in the genetic data with populations at Mt Etna, Cape Hillsborough, and Camooweal in Queensland and the Pilbara in Western Australia being highly divergent genetically and implies virtually no movement of individuals among these sites (Worthington-Wilmer et al. 1999). Recently expanded studies within the Pilbara have revealed strong structure between eastern and western populations (Armstrong et al. in prep). Populations within the Northern Territory and far north Queensland are also highly distinct from each other and other population centres, however, there is less structure among populations within these regions with the data implying greater connectivity occurring via male mediated gene flow (Worthington-Wilmer et al. 1999). While only two samples were obtained from the Kimberley region, one caught in the far west (Tunnel Creek) the other in the east (Cave Springs near Kununurra), sequence data showed the Kimberley bats were distinct not only from all other Australian populations but also from each other (Worthington-Wilmer 1996).

Population Trend
Decreasing
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Threats

Threats

Major Threats
This species is very vulnerable to disturbance in its roost sites. Cave tourism has been identified as a problem, but the most serious threat is from quarrying and reworking of old mine areas. In some cases, the collapse of disused mines may also be a threat. Habitat modifications for livestock may be a problem in some areas, as may competition for prey with introduced foxes and feral cats (Hutson et al. 2001). Barbed wire fences on cattle stations and lantana cause some direct mortality (Armstrong and Anstee 2000). For the populations at the southern limits of the species' range, the general paucity of suitable roost sites, the geographic distance between existing colonies, and the evident complete lack of gene flow indicates that these populations are totally isolated and will not be rescued by immigration or recolonised should local extinctions occur (J. Worthington-Wilmer pers. comm.).
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Management

Conservation Actions

Conservation Actions
The majority of known colonies occur in protected areas (e.g., national parks or heritage listed mine sites), however, there are a number of notable exceptions. The mine roosts the species relies on for breeding in the Pilbara region of Western Australia are not protected and no formal monitoring plan has been implemented (Armstrong and Anstee 2000; K. Armstrong pers. comm). The breeding populations at Claravale Station, Northern Territory and Kings Plains Station, north Queensland occur on private pastoral property with no conservation status (J. Worthington-Wilmer pers. comm.).

Current management activities take into account the results of population genetic studies, which have shown that colonies constitute separate metapopulations (Worthington-Wilmer et al. 1994, 1999). Activities include a captive breeding programme, long-term population studies and monitoring in Queensland, and population studies in Western Australia. In the late 1980s, a massive international campaign to prevent destruction of caves used by this bat at Mount Etna failed and this population has subsequently declined.

The species was evaluated in a Recovery Outline published in "The Action Plan for Australian Bats" (Duncan et al. 1999). That Action Plan downgraded the category of threat from Vulnerable to Lower Risk (near threatened) due to supposed uncertainty regarding the genetic boundaries for many of the known maternity sites and the inability to match Macroderma gigas to IUCN criteria. In 2001, apparently in response to the comments in the Action Plan, the species was delisted from the category of Vulnerable by the Australian federal government Threatened Species Scientific Committee, and no longer falls under the protection of the Commonwealth Government’s endangered species legislation. Legislation, however, in at least two of the three range states (Western Australia and Queensland) maintains Macroderma gigas in threatened or vulnerable categories (J. Worthington-Wilmer pers. comm.).

There is a need for increased regulation of cave tourism and visitation (B. Thomson pers. comm.). Mining companies are increasingly inserting non-barbed wire fences in crucial sections to avoid mortality (N. McKenzie pers. comm.). Identification and direct protection of unprotected maternity colonies is a priority. More ecological research and particularly identification of maternity sites is necessary (L. Lumsden pers. comm.).
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Relevance to Humans and Ecosystems

Benefits

Economic Importance for Humans: Negative

There are no significant negative effects of ghost bats.

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Economic Importance for Humans: Positive

Ghost bats are important in the control of rodents, especially introduced house mice, and other small mammals. They also produce guano, which can be used as a fertilizer.

Positive Impacts: produces fertilizer; controls pest population

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Wikipedia

Ghost Bat

The Ghost Bat (Macroderma gigas), also known as the False Vampire Bat is a bat endemic to Australia, named for the extremely thin membrane of its wings that makes it appear ghostly at night. Ghost Bats have grey fur on their backs and pale grey or white fur on their undersides. They have long, narrow wings but no tail, averaging 11 cm in length. Females are generally smaller than males. The adaptations of the ghost bats: They have large ears for long distance hearing, and very sharp teeth so they can attack prey.

The Ghost Bat is the only carnivorous bat in Australia and is also one of the largest microbats in the world.[2] It is largely insectivorous but will also consume frogs, lizards, and other small animals, including other bats. It hunts by sight as well as with echolocation. After killing its prey with its powerful bite, it carries it to a feeding perch to eat.

Ghost Bats inhabit northern Australia, from the east to the west coast. They roost in caves, mines, and tunnels in small colonies, usually of less than a hundred bats.

There are about 4000 to 6000 Ghost Bats in the wild. Females give birth to one young in September or November once every year. Ghost bats are considered to be vulnerable; their numbers declining due to the destruction of caves for mining, habitat clearing for agricultural use, and even cave tourism.

References

  1. ^ BirdLife International (2008). Macroderma gigas. In: IUCN 2008. IUCN Red List of Threatened Species. Downloaded on 24 February 2010.
  2. ^ Walker, Matt (3 June 2009). "'Nature's ghosts' caught on film". Earth News (BBC). http://news.bbc.co.uk/earth/hi/earth_news/newsid_8079000/8079476.stm. Retrieved 24 February 2010. 
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