Setirostris Explained

Setirostris eleryi is a species of small insectivorous bat found in inland eastern Australia. It is the sole species of the molossid genus Setirostris, a name that refers to the coarse bristles on their faces. Earlier common names have referred to this unique feature, and the 'free-tail' that is a common feature of its microchiropteran family, the Molossidae; no single common name emerged during the taxonomic revisions that identified what was referred to as the bristle-faced freetail.

Setirostris eleryi differs from all other bats in the family by possessing unique dentition and genital morphology, a distinctive echolocation call structure, and notably smaller body size of around 5g. The presence of stout bristles on the thin muzzle and face of S. eleryi distinguishes them from similar genus Ozimops, once regarded as "Mormopterus species", that previously included parts of the population. The description, first published in 2008, emerged from a comparison of morphological features with an earlier phylogenetic analysis that had indicated cryptic species amongst this poorly-known group of bats.

Setirostris eleryi may be widely distributed across inland Australia, ranging from very arid to moister subtropical regions. However, it is locally uncommon across its range, and only known to inhabit riparian zones and floodplains. During the day these bats roost in tree hollows of mature eucalypts, but are noted as squeezing themselves into other tiny crevices. They form colonies of up to twenty individuals, which often include bats of other species.

Taxonomy

A 1988 genetic study of species boundaries in Australian free-tailed bats (family Molossidae) indicated that species Setirostris eleryi, referred to as 'form sp 6' (later Mormopterus sp. 6), was one of eight distinct and unresolved genetic groups in the Australian population of Mormopterus. Mormopterus sp 6 was genetically distinct from all other types; however, only a single specimen from central Australia was included in the study. The acquisition of twenty-four additional specimens, from museum collections and by targeted trapping, facilitated a working description of Mormopterus sp. 6 in 2008 using a multi-locus analysis of morphology, the results of allozyme electrophoresis and investigation of echolocation call signatures. Referenced as an undescribed taxon, Mormopterus sp. 6 was cited by authors until its recognition as species Mormopterus (Setirostris) eleryi in publications after 2011.

Resolution of Australian Molossidae systematics showed that this species, and the east-coast Micronomus norfolkensis, are only distantly related to other Australian mollosid taxa. The differences between these two species and remaining taxa in the Mormopterus planiceps group', or planiceps–beccarii–loriae complex', previously published as an interim arrangement, led to the erection of four new subgenera in 2014. Prior to 2014, two subgenera were recognized within Mormopterus: subgenus Mormopterus and subgenus Micronomus. The two new subgenera included Setirostris, isolating this species as a monotypic taxon, and Ozimops, a subgenus containing seven other Australian taxa, as well as several Indo-Papuan taxa, all formerly in the planiceps group. Other mollosid populations were separated to the monotypic genus Micronomus and those outside of the same austral region remained within the subgenus Mormopterus. Subsequently, the rank of subgenus Mormopterus was itself revised, excluding the Australasian species, and elevated to the rank of genus.

The type specimen was collected at an elevation of near Eringa, a cattle pastoralist lease (station) close to the northern state border of South Australia.

The name Setirostris is derived from a combination of the Latin seta, meaning bristle, and rostrum, beak or snout, and refers to the characteristic bristles on the face; the gender is feminine. The specific name eleryi is for Elery Hamilton-Smith in recognition of contributions to bat research and conservation.

Common names for the species include hairy-nosed—or hairy-rostrum—free-tailed bat, bristle-faced freetail bat and Mormopterus sp. 6.

Description

Setirostris eleryi is a very small microchiropteran, with a light build, and was regarded as tiny when compared to species of Mormopterus, the genus of smaller bats in which they were variously placed. They have a mean weight of NaN5.2, a maximum weight of NaN8 and a forearm length from NaN31.5. The face and muzzle are relatively long and narrow. The muzzle and face are sparsely covered in fine hair, with the exception of a unique series of 26 to 30 conspicuous bristles on each side and a fringe of fur on the upper lip. The ears are triangular and are not joined across the forehead and the tragus is rounded. The dorsal colour ranges from sandy-brown to grey-brown with lighter coloration on the ventral surface.A prominent long and slender genital projection is present in both the male and female of the species. The function of the projection is unknown and these features are not shared by any other Australian Chiroptera[1] with the exception of Micronomus norfolkensis. Males of the species also possess unique serrated lateral flanges on the acutely pointed glans penis. Features of the dentition are also unique to this species.

As the type and sole species of genus Setirostris, S. eleryi is distinguished from other Molossid species, in particular those formerly placed in Mormopterus, by the absence of a developed gular sac, possessing two (rather than three) lower incisors and two (not one) upper premolars.

Range and distribution

Setirostris eleryi is uncommon and widely dispersed across broad areas of inland Australia, with specimens and records from central Australia and the remote southwestern corner of the Northern Territory, northern South Australia, western and central Queensland and northwestern and northern inland New South Wales (NSW). The distribution of S. eleryi is notable in that it ranges from extremely arid areas of the central Australian interior, where average annual rainfall is less than NaNinches200NaNinchesin (200in), to areas of the northeastern Queensland dry tropics where average annual rainfall can exceed NaNinches1000NaNinchesin (1000in). The eastern component of its distribution range occurs to the west of the Great Dividing Range within the Brigalow Belt (north and south), Mulga Lands, Darling Riverine Plains and Nandewar Biogeographic Regions.[2] In the western component it occurs within the Finke, MacDonnell Ranges, Simpson Strzelecki Dunefields and Central Ranges Bioregions.[2]

The presence of outlying records for S. eleryi at Kaltukatjara (southwestern Northern Territory), Mount Isa (northwestern Queensland) and in the area south of Bourke (northwestern New South Wales) indicate that the species may have a more extensive distribution in the arid and semi-arid regions of NSW, Queensland, the Northern Territory and Western Australia than available records indicate. However its range and status remain relatively poorly known. By 2008 it had been recorded at 26 localities and few additional locations have been recorded in subsequent years.

Habitat

Records of S. eleryi are of individuals captured in mist nets or harp traps in riparian habitats on ephemeral streams, floodways, pools or dams, usually at sites supporting a large fringe of eucalypt trees. Capture sites are consistently associated with riparian and floodplain habitats that support a canopy of eucalypts, including Eucalyptus camaldulensis, E. coolabah, E. microtheca, E. populnea, E. polyanthemos and E. citriodora. At Gundabooka National Park in western NSW the species was only trapped along drainage lines with eucalypts E. camaldulensis and E. populnea.[3] During radio tracking studies at the Gundabooka site the species was observed to preferentially forage along drainage lines and open channels, rarely moving into adjacent mulga vegetation dominated by Acacia aneura. All the roost sites identified were in tall eucalypts within, or adjacent to, riparian zones.

The preference of this species for riparian habitats is consistent across its known range. At the type locality in northern South Australia S. eleryi was captured on a floodway in Acacia cambagei low woodland with emergent Eucalyptus coolabah. At Idalia National Park in western Queensland two specimens were captured in riparian woodland near open water, with a canopy of Eucalyptus camaldulensis and Eucalyptus populnea. At a site in northeastern NSW (Kwiambal National Park) the bat was captured on a riparian terrace adjacent to a river, with trees at the location including Eucalyptus camaldulensis, Eucalyptus blakelyi and rough-barked apple, species Angophora floribunda.

Behaviour and ecology

The species is amongst the least known of Australian Chiroptera (bats), with little research and few records. Information on the behaviour and ecology of S. eleryi is mainly derived from a short study conducted at Gundabooka National Park in western NSW in 2005. The species has been captured in woodlands between Inverell and Yetman in northern inland NSW and at Cobar in western NSW.

Roost sites

Based on the limited observations, S. eleryi are known to maintain daytime roosts in tree hollows at a living or dead trunk or branch. All three roost known sites were in tall Eucalyptus populnea or Eucalyptus intertexta at a height of NaN3 above the ground and displayed very small NaN13 entrance holes leading to a larger chamber. The roosts were shared with between four and twenty other bats (including bats of other species) and in some cases roosts were used on consecutive nights. The roosts were located an average distance of NaN3.2 from capture sites and females were found to occupy separate maternity roosts.

Foraging and diet

Presumably, as is typical for similar species, S. eleryi emerge from their roosting sites and forage at night. The observations are along drainage lines and open channels, flying with slow fluttering movements below the canopy at a low altitude of 3mto4mm (10feetto13feetm). Prey items are noted as flying invertebrates, captured in the air close to the ground or adjacent vegetation by the chiropteran strategy that is similar to gleaning by birds. The specific composition of the invertebrate diet of S. eleryi is unknown. The flight patterns are distinguishable from similar species, as the slow flutter is closer to the foliage and ground.

Echolocation

The echolocation call of S. eleryi contrasts with all other Australian molossid bats in that it displays a strongly frequency-modulated search phase pulse. The bat also has the highest mean characteristic frequency (36 kHz) of any Australian Mormopterus.

Reproduction

Information on the reproduction of the S. eleryi is limited. A maternity roost located in December at Gundabooka National Park in western NSW contained a colony of fifteen lactating females. A female captured during October in the Northern Territory was in an advanced stage of pregnancy.

Conservation status and threats

Assessment and legislative status

As of 2020, S. eleryi is listed as a near-threatened species by the International Union for Conservation of Nature. It is listed as endangered in New South Wales and vulnerable in South Australia.[4] The regional status is a least concern species in the Northern Territory and Queensland, and 'not listed' in Australian Commonwealth conservation lists. The separation of the species to a monotypic taxon Setirostris, a subgenus or perhaps genus, indicates it is phylogenetically unique and this increases the conservation value of the population.

Population status

Setirostris eleryi appears to be extremely rare across its range.[5] It has been detected at a limited number of localities and at these sites it appears to be uncommon, often comprising less than two percent of the bats captured during surveys. In NSW it has only been recorded at a small number of locations, despite recent extensive surveys at over three hundred sites in suitable habitat.[5] Its preferred mode of foraging by flying at low levels along stream corridors suggests that the low numbers captured in surveys using mist nets and harp traps are an indication of rarity and are not an artifact of the survey methodology.[5]

Threats

Identified and potential threats to populations of S. eleryi are related to the direct and indirect actions of humans, including: land clearing,[5] timber harvesting, manipulation of water resources, altered fire regimes, use of pesticides, stocking with exotic ruminants, spread of feral animals and weeds, and atmospheric pollution leading to global warming.[6]

The most significant threat to S. eleryi is likely to be ongoing land clearing in semi-arid bioregions of Queensland and NSW.[5] The eastern Australian bioregions that comprise the core range of the species, particularly the Brigalow Belt (north and south), have been subjected to broad-scale clearing and habitat modification since European settlement. Clearing of vegetation for agriculture and removal of hollow bearing trees for firewood collection and forestry are likely to reduce the availability of roosting sites for S. eleryi.[5] Clearing of native vegetation and removal of dead wood and dead trees have been recognised as key threatening processes for the species in NSW.[5]

Additional key threatening processes that are considered likely to impact S. eleryi include: the alteration to natural flow regimes, competition from introduced western honey bees (Apis mellifera) for tree hollows, inappropriate fire regimes, reduction of invertebrate prey related to pesticide drift and lack of tree regeneration due to overgrazing and weeds.

Climate can influence bat distribution, movements and biogeography, access to food resources, timing of reproduction, and emergence and rate of energy expenditure.[6] [7] In combination with other factors, including ongoing loss and degradation of habitat, global climate change or global warming presents a serious and increasing threat to bats and other fauna.[6] The affinity of S. eleryi for riparian zones in arid and semi-arid environments renders it potentially vulnerable to the effects of water stress and extreme weather events.[6] Ecological factors that qualify the population as being at increased risk of the potential impacts of global climate change include: habitat (species that rely on riparian habitats in water stress prone environments), foraging type (aerial hawking insectivore), roost type (tree hollow specialist), biogeography (species with limited dispersal ability, limited ranging behaviour) and extreme weather (species that occur in regions where there is an increasing risk of extreme temperature events or changes in rainfall patterns).[6]

Conservation reserves

Setirostris eleryi has been recorded in a number of conservation reserves, including Gundabooka National Park (NSW),[3] Kwiambal National Park (NSW), Dthinna Dthinnawan National Park (NSW), Idalia National Park (QLD), Mariala National Park (QLD) and Witjira National Park (SA). The bioregions that are known to support S. eleryi populations in the eastern component of its range, as well as a subset of bioregions where it occurs in central Australia, display very low rates of land area reserved for conservation (less than five percent).[8] Based on locality data only 25% of sites known to support populations of S. eleryi are protected within conservation reserves.

External links

Notes and References

  1. Reardon, T. B. (2001). The unusual penis morphology of the hairy-nosed freetail bat. The Australasian Bat Society Newsletter 17: 53-54.
  2. Web site: Interim Biogeographic Regionalisation for Australia Version 7. Commonwealth of Australia . 2012.
  3. 10.7882/AZ.2001.006 . Ellis. M.. 1998. The first record of the Hairy-nosed Freetail Bat in New South Wales. Australian Zoologist. 31. 4. 608–609.
  4. Web site: South Australia National Parks and Wildlife Act 1972 Version 16.5.2013. Schedule 8 - Vulnerable species. Government of South Australia. 2018.
  5. Web site: Hairy-nosed Freetail Bat - endangered species listing. Adam. P.. 2004. NSW Government.
  6. Sherwin . H. A. . Montgomery . W. I. . Lundy . M. J. . 2012 . The impact and implications of climate change for bats . Mammal Review . 42 . 3 . 171–183 . 10.1111/j.1365-2907.2012.00214.x .
  7. Frick. W. F.. Stepanian. P. M.. Kelly. J. F.. Howard. K. W.. Kuster. C. M.. Kunz. T. H.. Chilson. P. B. . 2012. Climate and weather impact timing of emergence of bats. PLOS ONE. 7. 8. e42737. 10.1371/journal.pone.0042737. 22876331. 3411708. 2012PLoSO...742737F. free.
  8. Natural Resource Management Ministerial Council (2010). Australia's Strategy for the National Reserve System 2009–2030. Commonwealth of Australia.