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Yellow‐footed rock‐wallaby in Queensland 133


context may support higher goat populations, as shown by the significant relationship between mean effective distance to water and goat presence during the 2020s. By 2023, the EOO and AOO of the subspecies had both


increased because of recolonization of north-eastern sites. The EOO and AOO are likely to increase further by 2025, once 5 years have elapsed following the translocations made further north-east on Ravensbourne and these sites become eligible for inclusion in geographical range calcula- tions (Table 3; IUCN, 2022). However, because of the exis- tence of small subpopulations, ,10 suitable locations (as defined by the significant threat of goat competition), the population size of,10,000 and there being,1,000 animals in each subpopulation, as well as there being other known threats, P. xanthopus celeris remains eligible for categoriza- tion as Vulnerable under IUCN criteria B2ab(iii) and C2a(i) (Table 3). Habitat quality is predicted to decline because of the ongoing threat posed by goats, which have been intro- duced to numerous rock-wallaby localities since the erection of exclusion fences in the past decade. Given the evidence presented here, this is projected to result in declines of these rock-wallaby subpopulations. Potential P. xanthopus celeris habitat between the apparently isolated McGregor Range subpopulation and the main occurrence of the sub- species should be thoroughly surveyed, possibly via helicop- ter, which has proven to be an effective survey method in Idalia and Welford national parks (N. Finch, pers. comm., July 2023). Repeat surveys, including of a minimum subset of core monitoring sites, should occur approximately every decade to provide vital data on population trends and threats to inform future conservation management.


Author contributions Organization and leadership of the 2020s surveys, collation of data from the 1970s–2020s, writing: JLS; co-design of the original methodology, participation in the 1980s surveys, organ- ization and leadership of the 2010–2015 surveys: PDM; 2010s surveys: JLS, ICG, AH, TLW, DM; 2020s surveys: JLS, ICG, AH, JM, TLW, RJF, AJH; data analysis: RJF, AJH; writing and revision: all authors.


Acknowledgements Funding for this project was provided by Threatened Species Operations, Department of Environment, Science and Innovation, Queensland Government. Rodney Manthey, Neil Marks, David Akers, Ingrid Elmitt, Harry Macdermott, Boris Laffineur, Rod Fensham, Rosie Kerr, Shane Hume, Rebecca Richardson, Chloe Tully, Jim Wilson, Aisha Damali, Zainab Damali- Healy, Rowan Fairfax, Oliver Scully and Maree Tulley assisted with field surveys during 2010–2023. We thank the yellow-footed rock- wallaby researchers of the 1970s and 1980s, including Greg Gordon, Merv Parker, Gary Porter, Tony Paulsen, GordonWilkinson, Caroline Sandercoe, Jenny Curnow, Daryl Reimer, Ross Blick, G. Innes and K. Smith, for providing pioneering baseline data. Discussions with Ian Hume illuminated aspects of P. xanthopus celeris dynamics at Lisburne and Amaroo over the past 4 decades. Boris Laffineur accessed SILO data for the sites. Cameron Wilson provided a shapefile of exclusion fences. Jane McDonald commented on the text. We thank the land- holders andmanagers for their hospitality and interest in thismarsupial. JLSwas funded bytheNationalEnvironmental ScienceProgramthrough theThreatened SpeciesRecoveryHub during data collation, analysis and writing. PDM passed away suddenly in September 2018. We warmly


acknowledge his contributions to yellow-footed rock-wallaby research andconservationandhis loveof the backcountryofwesternQueensland.


Conflicts of interests None.


Ethical standards This research abided by the Oryx guidelines on ethical standards.


Data availability Survey data presented in this article are available in the Supplementary Material.


References


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Oryx, 2025, 59(1), 123–135 © The Author(s), 2024. Published by Cambridge University Press on behalf of Fauna & Flora International doi:10.1017/S0030605324000760


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