Coastal Tomb Bat - Taphozous australis
( Gould, 1854 )

 

 

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Subspecies: Unknown
Est. World Population: 9000-10000

CITES Status: NOT LISTED
IUCN Status: Near Threatened
U.S. ESA Status: NOT LISTED

Body Length:
Tail Length:
Shoulder Height:
Weight:

Top Speed:
Jumping Ability: (Horizontal)

Life Span: in the Wild
Life Span: in Captivity

Sexual Maturity: (Females)
Sexual Maturity: (Males)
Litter Size:
Gestation Period:

Habitat:
This species roosts in sea caves, rocky clefts, rockpiles (e.g. at Cape Melville), old buildings, mines and WWII bunkers. Most roosts are shallow and partially lit. Foraging occurs within a few kilometres of the coast of the mainland, in areas of coastal dune scrubland, paperbark swamps, rainforest, closed and open eucalypt forest, and mangroves. They have been observed foraging above lights near remnant bushland, and up to 15 km from their roosts. Bats from island colonies have been observed to fly 2.5 km to the mainland to forage above mangroves and rainforest in preference to foraging over nearby islands (Woinarski et al. 2014).

Range:

This species has been recorded from Australia and Papua New Guinea, with an elevational range between sea level and 300 m asl. In Australia, it is generally restricted to coastal and near-coastal areas in northern and eastern Queensland from Shoalwater Bay to the tip of Cape York Peninsula, and the Torres Strait Islands (Duncan et al. 1999, Richards 2008, Woinarski et al. 2014). Within this range it occurs as a series of colonies in sea caves and rocky coastal clefts. In the southern part of the range it is largely restricted to a 3 km coastal band, but on Cape York Peninsula cave roosts have been detected further inland. Older surveys discovered colonies in more than 100 of 600 sea caves searched between Townsville and Cooktown (Duncan et al. 1999). Area of occupancy may be most appropriately determined by the total number of breeding sites (roost caves), however extensive surveys are needed to fully characterise colony occurrence (Woinarski et al. 2014).

Evidence for its presence in Papua New Guinea comes only from three historical records. Dobson’s (1878) record from Port Moresby was suggested to be an erroneous record by Koopman (1982). Two specimens in the Australian Museum collected in the late 1800s by the Royal Geographical Society Expedition do not have an associated collection locality but are likely from the Lower Strickland River that was the focus of the expedition (Flannery 1995, Bonaccorso 1998).


Conservation:
It has been recorded from the Hillsborough National Park in Australia, where populations have recently declined, and several other coastal and island national parks. This species is probably most vulnerable at its roosts. There is a need to identify and protect important roosting sites and foraging habitat for this species. Further studies are also needed into of the distribution, genetic population structure, movements while foraging and movements between the mainland coast and offshore islands, abundance, and threats to the species.

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