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15 results for “Isoodon”
Fig. 4 in Confirmation of a unique species of Giardia, parasitic in the quenda (Isoodon obesulus)
Fig. 4. Phylogenetic relationships of Giardia peramelis isolates obtained in this study (quenda QBN13, QM22, QBY95) with published reference material available at the ITS1-5.8SITS2 locus. Evolutionary history inferred using the neighbour-joining method supported with bootstrap test of 1000 replicates (values> 50% shown). G. muris is used as the out group.
Fig. 3 in Confirmation of a unique species of Giardia, parasitic in the quenda (Isoodon obesulus)
Fig. 3. Phylogenetic relationships of Giardia peramelis isolates obtained in this study (quenda QBN13, QM22, QBY95) with published reference material available at the 18s rRNA locus. Evolutionary history inferred using the neighbour-joining method supported with bootstrap test of 1000 replicates (values> 50% shown). G. muris is used as the out group.
Fig. 1 in Anthropozoonotic significance, risk factors and spatial distribution of Giardia spp. infections in quenda (Isoodon obesulus) in the greater Perth region, Western Australia
Fig. 1. Geographical distribution of Giardia spp. infection in Perth quenda. Quenda were mapped using the GPS position of the location at which they were trapped. GPS points are jittered, and icons for uninfected quenda are 50% transparent, to improve visualisation of the relative distribution of Giardia spp. infection. By Kulldorff's spatial scan statistic, the circle in the north-west region represents a cluster of relatively decreased Giardia spp. infection risk in Perth quenda (OR of infection <0.001, compared to quenda trapped elsewhere in Perth; p <0.001).
Fig. 4 in Characterising a sarcoptic mange epizootic in quenda (Isoodon fusciventer)
Fig. 4. Density of sarcoptic mange cases in quenda (Isoodon fusciventer) and potential outbreak extent in Roleystone, Perth, Western Australia from July 2019 to June 2021.
Fig. 2 in Characterising a sarcoptic mange epizootic in quenda (Isoodon fusciventer)
Fig. 2. Frequency of infestation by location on the body recorded from 26 quenda (Isoodon fusciventer) with sarcoptic mange admitted to care at Darling Range Wildlife Shelter from Roleystone, Perth, Western Australia from July 1, 2019 to June 30, 2021. (Image: Katerina Ryabtseva).
Fig. 3 in Characterising a sarcoptic mange epizootic in quenda (Isoodon fusciventer)
Fig. 3. Common clinical signs of sarcoptic mange in quenda (Isoodon fusciventer) from Roleystone, Perth, Western Australia in animals admitted to Darling Range Wildlife Shelter between July 1, 2019 and June 30, 2021. A: The early consolidation phase of the disease, with visible erythema and alopecia on rump, flanks and paws and lesions developing on the face; B: Alopecia and emaciation in a quenda undergoing treatment; C: Severe chronic disease evident by extensive deep fissures throughout the epidermis, emaciation, hyperkeratosis, alopecia and lethargy; D: Papillomatous lesions on the posterior dorsal region of a quenda undergoing treatment for sarcoptic mange. (Images: Darling Range Wildlife Shelter).
Fig. 1 in Characterising a sarcoptic mange epizootic in quenda (Isoodon fusciventer)
Fig. 1. Prevalence of sarcoptic mange in population groups of quenda (Isoodon fusciventer) admitted to care from Roleystone, Western Australia between July 1, 2019 and June 30, 2021.
Fig. 1 in A review and comparison of the nematode assemblages of the Australian golden bandicoot, Isoodon auratus, the quenda, I. fusciventer and southern brown bandicoot, I. obesulus (Peramelidae), from material held in the south Australian museum
Fig. 1. Map of Australia showing the distributions of Isoodon auratus (green), Isoodon fusciventer (yellow) and Isoodon obesulus (blue). Abbreviations: NT Northern Territory; NSW New South Wales; Qld Queensland; SA South Australia; Tas Tasmania; Vic Victoria; WA Western Australia. (For interpretation of the references to colour in this figure legend, the reader is referred to the Web version of this article.)
Fig. 1 in Isoodon obesulus (Peramelemorphia: Peramelidae)
Fig. 1.—An adult male Isoodon obesulus from Tinderbox, Tasmania, in May 1979. Used with permission of the photographer, Hans Wapstra.
Fig. 2 in Isoodon obesulus (Peramelemorphia: Peramelidae)
Fig. 2.—Dorsal, ventral, and lateral views of skull and lateral view of mandible of an adult female Isoodon obesulus (Tasmanian Museum and Art Gallery, Accession Number A705) from Lymington, Tasmania, 9 June 1965; A. Halton. Greatest length of skull is 63.9 mm.
Simulating genetic mixing in strongly structured populations of the threatened southern brown bandicoot (Isoodon obesulus)
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Fig. 1 in Confirmation of a unique species of Giardia, parasitic in the quenda (Isoodon obesulus)
Fig. 1. Cyst of Giardia peramelis-light microscopy.
Prioritising source populations for supplementing genetic diversity of reintroduced southern brown bandicoots Isoodon obesulus obesulus
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Bandicoots return to Booderee: initial survival, dispersal, home range and habitat preferences of reintroduced southern brown bandicoots (eastern sub species; Isoodon obesulus obesulus)
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.
Bandicoots return to Booderee: initial survival, dispersal, home range and habitat preferences of reintroduced southern brown bandicoots (eastern sub species; Isoodon obesulus obesulus)
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