Nest protection for threatened birds 99
impacts and return on investment of the other interventions (Williams et al., 2011). The modest improvements in recruitment rates under
realistic detection scenarios and best estimates for nest suc- cess prompted broader discussion amongst workshop participants about other ideas, including increased invest- ment and effort in the detection of birds, a wider explo- ration of audible and subaudible acoustic control to displace mammalian and (possibly) avian predators, and the use of chemical/acoustic misinformation techniques to deter predators. Additionally, fire, fuel and landscape management should form part of the overall strategy for the recovery of the species. During extreme weather events, removing nestlings (or
parents and nestlings) from the wild to avoid their death may be warranted. However, this type of intervention would have significant logistical implications (e.g. cost, and time to hand-rear birds) and the risk of potential behavioural modifications if nestlings were to be removed from their parents. However, this option may need to be considered if the species continues to exhibit poor nest success in the wild and/or if conditions deteriorate, and it may be appropriate to remove breeding pairs and then later translocate fledglings/adults within the release programme. Monitoring of the effectiveness and performance of any intervention will be required (Possingham et al., 2001). This would provide evidence for whether the intervention or action should continue. In the breeding season of 2023 and 2024, there was a range of nest protection measures implemented to monitor birds and predators. In addition, we are currently investigating the use of ultrasonic deter- rents to temporarily displace squirrel/sugar gliders from regent honeyeater nests, and research how mammalian predators use smell to find avian prey. Our findings from these actions will be published in due course. Conservation management of the regent honeyeater
over the next 5 years will be critical to the persistence of the species, and having a process for prioritizing actions when there is a high degree of both urgency and uncertainty is important. Nest protection is a crucial pathway for ar- resting decline in regent honeyeaters (Heinsohn et al., 2022). Our study suggests that, with parallel investment in improved nest detection, it is possible that nest protec- tion can provide a pathway for recovery of this species.
Acknowledgements We acknowledge the Traditional Custodians of the lands on which this research was conducted and recognize their care of and connection to Country. We thank R. Crates for his contribution to the discussion on regent honeyeaters and those who participated in the brainstorming, pre-elicitation, expert elicitation and future planning meetings. The decision-making workshops were supported by an Environmental Restoration Fund Grant issued by the Australian Government’s Department of Agriculture, Water and Environment and the Australian Government’s Environment
Restoration Fund. We also acknowledge funding from the Winifred Violet Scott Charitable Trust in support of this research.
Author contributions Project conception, data collection: JST, DI; decision analysis: TW; idea development, conclusions, writing: all authors.
Conflicts of interest None
Ethical standards As no animals were used in this research, no specific ethical approval or licencing were required, and we other- wise abided by the Oryx guidelines on ethical standards.
Data availability Data is available upon reasonable request to the corresponding author.
References
BEDFORD,T.&COOKE, R.M. (2001) MathematicalTools for Probabilistic Risk Analysis. Cambridge University Press, Cambridge, UK.
BIRDLIFE INTERNATIONAL (2018) Anthochaera
phrygia.In The IUCN Red List of Threatened Species 2018.
dx.doi.org/10.2305/IUCN.UK. 2018-2.RLTS.T22704415A130992272.en.
BOLAM, F.C., GRAINGER, M.J., MENGERSEN, K.L., STEWART, G.B., SUTHERLAND,W.J., RUNGE, M.C. & MCGOWAN, P.J.K. (2019) Using the value of information to improve conservation decision making. Biological Reviews, 94, 629–647.
BURGMAN, M.A. (2016) Trusting Judgements: How to Get the Best Out of Experts. Cambridge University Press, Cambridge, UK.
BURGMAN, M.A.,CARR, A.,GODDEN, L.,GREGORY, R.,MCBRIDE, M., FLANDER,L.&MAGUIRE,L. (2011) Redefining expertise and improving ecological judgment. Conservation Letters, 4, 81–87.
CANESSA, S., TAYLOR, G., CLARKE, R.H., INGWERSEN, D., VANDERSTEEN,J.&EWEN, J.G. (2020) Risk aversion and uncertainty create a conundrum for planning recovery of a Critically Endangered species. Conservation Science and Practice, 2,e138.
CAREY, J.M. & BURGMAN, M.A. (2008) Linguistic uncertainty in qualitative risk analysis and how to minimize it. Annals of the New York Academy of Sciences, 1128, 13–17.
COMMONWEALTH OF AUSTRALIA (2014) Listing advice – Aggressive exclusion of birds from potential woodland and forest habitat by over-abundant noisy miners.
environment.gov.au/biodiversity/ threatened/key-threatening-processes/overabundant-noisy-miners [accessed December 2024].
CONROY, M.J. & PETERSON, J.T. (2013) Decision Making in Natural Resource Management: A Structured, Adaptive Approach. John Wiley & Sons, Chichester, UK.
CRATES, R., MCDONALD, P.G., MELTON, C.B., MARON, M., INGWERSEN, D., MOWAT, E. et al. (2023) Towards effective management of an overabundant native bird: the noisy miner. Conservation Science and Practice, 5,e12875.
CRATES, R., OLAH, G., ADAMSKI, M., AITKEN, N., BANKS, S., INGWERSEN, D. et al. (2019a) Genomic impact of severe population decline in a nomadic songbird. PLOS One, 14,e0223953.
CRATES, R., RAYNER, L., STOJANOVIC, D., SCHEELE, B.C., ROFF, A., MACKENZIE,J. & HEINSOHN,R. (2022) Poor-quality monitoring data underestimate the impact of Australia’s megafires on a Critically Endangered songbird. Diversity and Distributions, 28, 506–514.
CRATES, R., RAYNER, L., STOJANOVIC, D.,WEBB, M., TERAUDS,A.& HEINSOHN,R. (2019b) Contemporary breeding biology of Critically Endangered regent honeyeaters: implications for conservation. Ibis, 161, 521–532.
Oryx, 2025, 59(1), 91–100 © The Author(s), 2024. Published by Cambridge University Press on behalf of Fauna & Flora International doi:10.1017/S0030605324000942
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