How many mature microhabitats does a slow-recolonising reptile require? Implications for restoration of bauxite minesites in south-western Australia

2011 ◽  
Vol 59 (1) ◽  
pp. 9 ◽  
Author(s):  
Michael D. Craig ◽  
Angela M. Benkovic ◽  
Andrew H. Grigg ◽  
Giles E. St J. Hardy ◽  
Patricia A. Fleming ◽  
...  
Keyword(s):  
Home Range ◽  
Western Australia ◽  
Suitable Habitat ◽  
Home Ranges ◽  
Random Samples ◽  
Successional Species

If we are to accelerate the recolonisation of restored areas by slow-recolonising species, we must provide suitable microhabitats at appropriate densities. Previous research in south-western Australia has shown that Napoleon’s skink (Egernia napoleonis) rarely recolonises restored areas. We trapped Napoleon’s skink in restoration and unmined forest to confirm the species was late successional. We also radio-tracked six skinks in unmined forest, to determine types and characteristics of used microhabitats, and estimated home ranges to determine required microhabitat densities, with the aim of accelerating skink recolonisation of restored areas. All tracked skinks used logs and hollow-bearing trees. Used logs were larger, and used trees were larger and taller than random samples, probably because large logs and trees were more likely to contain cracks and hollows that provide a refuge from predators. Extrapolations from home-range estimates indicated that a minimum of four logs ha–1 are required in restored areas to facilitate recolonisation by skinks, with skink densities likely to increase with log densities. Our study demonstrated that not all fauna will naturally recolonise restored areas and management of these areas is required to provide suitable habitat for late-successional species. Our approach could potentially be applied to other ecosystems or species.

scholarly journals Western Bristlebird Dasyornis longirostris: Response to fire and persistence of home range in the Fitzgerald River National Park, Western Australia

2021 ◽  
Vol 38 ◽  
pp. 172-192
Author(s):  
Shapelle McNee ◽  
Brenda Newbey ◽  
Sarah Comer ◽  
Allan Burbidge ◽  
◽  
...  
Keyword(s):  
Home Range ◽  
Western Australia ◽  
National Park ◽  
Fire Management ◽  
Suitable Habitat ◽  
Home Ranges ◽  
Habitat Condition ◽  
Management Actions ◽  
Burnt Areas ◽  
Western Australian

We investigated the response of the Western Bristlebird Dasyornis longirostris to fire in the Fitzgerald River National Park (FRNP), Western Australia, over a 34-year period. This species is a threatened Western Australian endemic restricted to a highly fire-prone habitat. Commencing in 1985, we surveyed for occurrence of Western Bristlebirds within the FRNP. Monitoring that was specifically focused on fire impacts began at Fitzgerald Track in November 1994 following a fire the previous month. That site had been surveyed in June and August 1994 before the fire. Fires in other recently surveyed locations in 1997–1998, 2000, 2008 and 2019 allowed for comparisons to be made following further monitoring of these sites. Many Bristlebirds survived a fire then relocated along or near the fire edge, usually in clusters of home ranges where suitable habitat was available. Bristlebirds gradually re-occupied burnt areas when these became suitable, often to home ranges occupied before the fire. There was a tendency for a home range to be occupied for >1 year. A change independent of fire could occur. Areas of vegetation of different fire ages were used by Bristlebirds for differing time periods. Sites in the lower-rainfall areas required longer periods of time for habitat to be recolonised by Bristlebirds and the maximum age of vegetation occupied by Bristlebirds varied between sites. For these reasons, generalised prescriptions are not appropriate, but fire management of individual patches of Bristlebird habitat in the FRNP can be guided by these findings, ensuring that unburnt refuge areas are both protected and retained, with the timing of management actions informed by knowledge of population response and habitat condition.

Population dynamics of the Quokka, Setonix brachyurus, on the west end of Rottnest I., Western Australia I. Habitat and distribution of the quokka

1967 ◽  
Vol 15 (1) ◽  
pp. 29 ◽  
Author(s):  
WN Holsworth
Keyword(s):  
Population Dynamics ◽  
Home Range ◽  
Western Australia ◽  
Major Portion ◽  
Home Ranges ◽  
Group Affiliation ◽  
The West

Data collected over a period of 10 yr is presented on the distribution of a small wallaby, the quokka, on the isolated West End portion of Rottnest I., Western Australia. The density of quokkas in each locality varied with the density of grasses that composed the major portion of their diet. Generally, the animals are non-gregarious and each quokka has a home range of about 10 ac. The home ranges of groups of 25-150 individuals overlap to form group territories. The boundaries of the group territories are stable and in places coincide with topographical features. Young quokkas usually remain in their natal group territory and rarely do permanent changes in group affiliation by animals of any age occur even after the population of adjacent territories has been greatly reduced.

scholarly journals Bandicoots return to Booderee: initial survival, dispersal, home range and habitat preferences of reintroduced southern brown bandicoots (eastern sub species; Isoodon obesulus obesulus)

2018 ◽  
Vol 45 (2) ◽  
pp. 132 ◽  
Author(s):  
N. M. Robinson ◽  
C. I. MacGregor ◽  
B. A. Hradsky ◽  
N. Dexter ◽  
D. B. Lindenmayer
Keyword(s):  
Home Range ◽  
Body Mass ◽  
National Park ◽  
Effective Means ◽  
Habitat Preferences ◽  
Home Range Size ◽  
Suitable Habitat ◽  
Home Ranges ◽  
Vegetation Types ◽  
Eastern Australia

Context Reintroductions can be an effective means of re-establishing locally extinct or declining faunal populations. However, incomplete knowledge of variables influencing survival and establishment can limit successful outcomes. Aim We aimed to examine the factors (e.g. sex, body mass, release order) influencing the survival, dispersal, home range and habitat selection of reintroduced southern brown bandicoots (eastern subspecies; Isoodon obesulus obesulus) into an unfenced, predator-managed environment in south-eastern Australia (Booderee National Park). Methods Over 2 weeks in May 2016, six female and five male bandicoots were wild-caught in state forest and hard released into the park. Release locations were approximately evenly distributed between three primary vegetation types assessed as suitable habitat: heath, woodland and forest. Bandicoots were radio-tracked day and night for 4 weeks from the initial release date. Key results No mortality was detected. Males dispersed more than twice as far as females (male 704 m, female 332 m), but there was no significant sex bias in home range size. At the landscape scale, bandicoots preferentially selected home ranges that contained heath and avoided forest. Within home ranges, heath and woodland were both favoured over forest. Conclusions Post-release dispersal is sex-biased, but more data are required to determine the influence of other predictors such as body mass and release order. Within the release area, bandicoots favoured non-forest vegetation types. Implications Our study outlines factors influencing the establishment of reintroduced bandicoots. We recommend that future bandicoot reintroductions to Booderee National Park occur within areas of heath and woodland, and that subsequent releases consider the potentially larger spatial requirements and conspecific avoidance among male bandicoots. Our findings contribute new knowledge for improving translocation methods of a nationally endangered medium-sized mammal.

scholarly journals Home Ranges and Spatial Organization of Fishers, Martes pennanti, in Central British Columbia

2009 ◽  
Vol 123 (2) ◽  
pp. 126 ◽  
Author(s):  
Richard D. Weir ◽  
Alton S. Harestad ◽  
Fraser B. Corbould
Keyword(s):  
British Columbia ◽  
Home Range ◽  
Spatial Organization ◽  
Home Range Size ◽  
Range Size ◽  
Suitable Habitat ◽  
Home Ranges ◽  
Martes Pennanti ◽  
Utilization Distribution ◽  
Minimum Convex Polygon

We described the size and spatial arrangement of aggregate and seasonal home ranges for 17 radio-tagged resident Fishers (Martes pennanti) that were >1.5 years old in two areas of central British Columbia during 1990-1993 and 1996-2000. We estimated home range size for each Fisher from the 95% isopleth of the utilization distribution generated using a fixed kernel model with smoothing selected by least-squares cross-validation (95% FK). For comparison to previous studies, we also calculated the minimum convex polygon estimate of home range size (MCP) for each animal. The aggregate home ranges (95% FK) of female Fishers (mean = 37.9 km², SD = 18.5, range = 10.5 – 81.2, n = 11) were significantly smaller than those of males (mean = 161.3 km², SD = 100.0, range = 46.0 – 225.2, n = 3; P = 0.019). We observed minor overlap among 95% FK home ranges of Fishers of the same sex, but considerable overlap among home ranges of males and females. Home ranges (95% FK or MCP) that we observed in central British Columbia were larger than those reported elsewhere in North America, particularly for males. We suggest that the distribution of resources for Fishers may occur at lower gross densitiesin central British Columbia than in other portions of the Fisher’s range and that suitable habitat in which Fishers can establish home ranges is not found uniformly across the landscape.

Successful reintroduction of the brushtail possum to Wadderin Sanctuary in the eastern wheatbelt of Western Australia

2014 ◽  
Vol 36 (2) ◽  
pp. 229 ◽  
Author(s):  
Jeff Short ◽  
Andrew Hide
Keyword(s):  
Western Australia ◽  
Early Age ◽  
Brushtail Possum ◽  
Suitable Habitat ◽  
Home Ranges ◽  
Annual Average ◽  
Initial Release ◽  
Average Rainfall ◽  
Ready Availability ◽  
Extant Population

The brushtail possum (Trichosurus vulpecula) was reintroduced to the fox-free habitat of the Wadderin Sanctuary in the eastern wheatbelt of Western Australia in 2008. Subsequent monitoring through to 2013 has revealed a small but healthy extant population that occupies all suitable habitat with some animals moving beyond the predator-free sanctuary to adjoining woodland patches. Possums occurred at a low density and had large home ranges relative to other studies at more mesic sites elsewhere. This is likely linked to the low productivity of the site (annual average rainfall of 332 mm) and one-way dispersal of young across the barrier fence. Possums preferentially occupied woodlands of York gum and salmon gum, utilised rock she-oak habitat, but made little use of shrubland and mallee habitats within the sanctuary. Female possums appeared to mature at an early age and to have young for much of the year. Recruitment was biased towards males in the first four years of establishment; although many appeared to rapidly disappear from the population. The success of this reintroduction is most likely linked to the initial release of possums into vacant habitat, the absence of foxes, and the ready availability of hollows in mature eucalypts and shelter sites in rock crevices.

Home range, habitat suitability and population modelling of feral Indian peafowl (Pavo cristatus) on Kangaroo Island, South Australia

2016 ◽  
Vol 64 (2) ◽  
pp. 107 ◽  
Author(s):  
Calum X. Cunningham ◽  
Thomas A. A. Prowse ◽  
Pip Masters ◽  
Phillip Cassey
Keyword(s):  
Home Range ◽  
Habitat Suitability ◽  
South Australia ◽  
Ecological Impacts ◽  
Suitable Habitat ◽  
Home Ranges ◽  
Pest Species ◽  
Population Modelling ◽  
Demographic Models ◽  
Pavo Cristatus

The Indian peafowl (Pavo cristatus) is a declared alien pest species on Kangaroo Island, South Australia, where it is implicated in a range of social problems and potential ecological impacts. To inform the management of feral peafowl, we aimed to (1) provide an estimate of peafowl distribution and abundance; (2) measure peafowl home ranges; (3) calculate the area of suitable peafowl habitat; and (4) estimate how the population could change under various culling scenarios. Using expert and landholder surveys, we estimated that ~380 individuals (range 330–428) were distributed among 21 separate groups on Kangaroo Island. Habitat suitability modelling identified native vegetation near agriculture as the preferred peafowl habitat and indicated that substantial unoccupied suitable habitat is available. The mean home range of eight peafowl was 52 ha and one dispersal event of 4.5 km demonstrated that unoccupied suitable habitat could feasibly be colonised. Demographic models indicated that, if unmanaged, the peafowl population could exceed 2000 individuals after 10 years, but that culling ~85 individuals annually could maintain the current population size. We therefore suggest that control of the Kangaroo Island peafowl population is warranted while the current distribution of peafowl is well understood.

Home Range Shift and Dispersal of Red Deer: Implications for Establishing Nature Reserve Networks in China

2014 ◽  
Vol 955-959 ◽  
pp. 2600-2606 ◽  
Author(s):  
Wei Dong Bao ◽  
Xu Wei Zhou ◽  
Shu Li Zhang ◽  
Kun Shi
Keyword(s):  
Home Range ◽  
Red Deer ◽  
Nature Reserve ◽  
Young Male ◽  
Biosphere Reserve ◽  
Range Shift ◽  
Suitable Habitat ◽  
Home Ranges ◽  
Reserve Network ◽  
Autumn And Winter

The establishment of nature reserves is critical for saving endangered wild animal species, however, most of the reserves are separated by human settlements in China. It is unknown that how those animals inside the reserve adapted to the isolated environment in habitat use and dispersal. We studied red deer seasonal home range and dispersal by radio-tracking from 2006 to 2011 at Saihanwula Biosphere Reserve, Inner Mongolia. The results showed that home range sizes of female deer had seasonal differences with the smallest range in autumn and largest in spring which was different from home range variation of red deer in Europe. Home ranges overlapped between female deer, particularly in autumn and winter seasons. A young male showed dispersal behavior, several times during dispersal period it tried to find suitable habitat outside of the reserve. Our results indicated that a connected nature reserve network is needed to protect wild ungulates in China.

scholarly journals Impact of natural salt lick on the home range of Panthera tigris at the Royal Belum Rainforest, Malaysia

2021 ◽  
Vol 11 (1) ◽  
Author(s):  
Bryan Andrew Lazarus ◽  
Azlan Che-Amat ◽  
Muhammad Muzammil Abdul Halim Shah ◽  
Azwan Hamdan ◽  
Hasliza Abu Hassim ◽  
...  
Keyword(s):  
Home Range ◽  
Prey Availability ◽  
Nutritional Ecology ◽  
Camera Traps ◽  
Home Ranges ◽  
Panthera Tigris ◽  
Health Maintenance ◽  
Salt Lick ◽  
Save Energy ◽  
Salt Licks

AbstractNatural salt lick (sira) is a strategic localisation for ecological wildlife assemblage to exhibit geophagy which may act as a population dynamic buffer of prey and predators. Undoubtedly, many agree that geophagy at natural licks is linked to nutritional ecology, health and assembly places facilitating social interaction of its users. Overall, natural salt licks not only save energy of obtaining nutrient leading to health maintenance but also forms the basis of population persistence. The Royal Belum Rainforest, Malaysia (Royal Belum) is a typical tropical rainforest in Malaysia rich in wildlife which are mainly concentrated around the natural salt lick. Since this is one of the most stable fauna ecology forest in Malaysia, it is timely to assess its impact on the Malayan tiger (Panthera tigris) home range dynamics. The three-potential home ranges of the Malayan tiger in this rainforest were selected based on animal trails or foot prints surrounding the salt lick viz (e.g. Sira Kuak and Sira Batu; Sira Rambai and Sira Buluh and Sira Papan) as well as previous sightings of a Malayan tiger in the area, whose movement is dependent on the density and distribution of prey. Camera traps were placed at potential animal trails surrounding the salt lick to capture any encountered wildlife species within the area of the camera placements. Results showed that all home ranges of Malayan tiger were of no significance for large bodied prey availability such as sambar deer (Rusa unicolor), and smaller prey such as muntjacs (Muntiacus muntjac) and wild boar (Sus scrofa). Interestingly, all home range harbour the Malayan tiger as the only sole predator. The non-significance of prey availability at each home range is attributed to the decline of the Malayan tiger in the rainforest since tigers are dependant on the movement of its preferred prey surrounding natural salt licks. Thus, the information from this study offers fundamental knowledge on the importance of prey-predator interaction at salt lick which will help in designing strategy in rewilding or rehabilitation programs of the Malayan tiger at the Royal Belum Rainforest.

The spatial dynamics of White-browed Babbler groups in a fragmented agricultural landscape

2002 ◽  
Vol 8 (4) ◽  
pp. 271 ◽  
Author(s):  
Peter G. Cale
Keyword(s):  
Home Range ◽  
Breeding Season ◽  
Group Dynamics ◽  
Agricultural Landscape ◽  
Local Population ◽  
Breeding Site ◽  
Home Ranges ◽  
Effective Population ◽  
Study Sites ◽  
Group Movements

White-browed Babbler Pomatostomus superciliosus groups occupying linear strips of vegetation had breeding territories that were smaller in area and had longer linear dimensions than those occupying patches. A group's non-breeding home range was larger than its breeding territory. Groups occupying linear/patch home ranges expanded the linear extent and area of their home ranges more than those within other home range configurations. Some groups moved during the non-breeding season and this was more likely to occur if the group occupied a remnant with a low abundance of invertebrates during summer. Some groups that moved returned prior to the next breeding season, but the majority were never seen again. New groups moved into the study sites and established in vacant home ranges. This suggests that those groups that left the study sites may have established new home ranges elsewhere. Breeding site fidelity was lower in groups that had failed in previous breeding attempts. Therefore, group movements were influenced by the feeding and breeding quality of the habitat. However, the configuration of the local population also influenced group movements with those groups on the edge of a local population being more likely to move than those in the interior. New groups were formed by two processes; group dispersal, where groups generally filled a vacant home range, and group budding, which involved the splitting of a large group. Group dispersal maintained group densities while group budding increased the density of groups in a local population. These two processes were common, producing localized fluctuations in the density of groups. Since babbler groups contain only one breeding pair, changes in group density represent changes in effective population size. Therefore, group dynamics may be important to the persistence of local populations of White-browed Babblers, especially in landscapes that have suffered from habitat loss and fragmentation.

Koalas continue to occupy their previous home-ranges after selective logging in Callitris - Eucalyptus forest

2007 ◽  
Vol 34 (2) ◽  
pp. 94 ◽  
Author(s):  
Rodney P. Kavanagh ◽  
Matthew A. Stanton ◽  
Traecey E. Brassil
Keyword(s):  
Home Range ◽  
Basal Area ◽  
Selective Logging ◽  
Home Ranges ◽  
Phascolarctos Cinereus ◽  
Eucalyptus Forest ◽  
South Wales ◽  
Callitris Glaucophylla ◽  
One Year ◽  
Cypress Pine

The koala (Phascolarctos cinereus) is a charismatic, high-profile species whose conservation needs are commonly perceived to be incompatible with logging. However, koala biology and the results of chronosequence studies elsewhere suggest that this species may tolerate a degree of habitat alteration caused by logging. In this study, 30 koalas, five in each of six areas available for logging within a mixed white cypress pine (Callitris glaucophylla)–Eucalyptus forest in north-western New South Wales, were radio-tracked for one year during 1997–1998 to determine their movements, home-range sizes and tree preferences. Five months after the study began, three of these areas were logged selectively for sawlogs and thinnings of the white cypress pine, a tree that is important to koalas for daytime shelter. This removed about one-quarter of the stand basal area, but the eucalypt component was unaffected. The remaining three areas were left undisturbed as controls. Radio-tracking continued in all six areas for another seven months. Koalas continued to occupy all or part of their previous home-ranges after selective logging, and home-range sizes remained similar between logged and unlogged areas. Home-ranges for both sexes overlapped and were ~12 ha for males and 9 ha for females. Koala survival and the proportions of breeding females were similar in logged and unlogged areas. The principal food trees of the koala were red gums, mainly Eucalyptus blakelyi and E. chloroclada, and the pilliga box (E. pilligaensis), none of which were logged in this study. These results suggest that selective logging for white cypress pine does not appear to adversely affect koala populations and that koalas may not be as sensitive to logging as previously thought. Further work is required to determine thresholds in the level of retention of koala food trees in logging operations.

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