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Wildlife Research Wildlife Research Society
Ecology, management and conservation in natural and modified habitats
RESEARCH ARTICLE (Open Access)

Can flexible timing of harvest for translocation reduce the impact on fluctuating source populations?

Simon J. Verdon https://orcid.org/0000-0002-3923-2242 A B D , William F. Mitchell https://orcid.org/0000-0003-2212-2562 C and Michael F. Clarke A B
+ Author Affiliations
- Author Affiliations

A Research Centre for Future Landscapes, La Trobe University, Kingsbury Drive, Melbourne, Vic. 3086, Australia.

B Department of Ecology, Environment and Evolution, La Trobe University, Kingsbury Drive, Melbourne, Vic. 3086, Australia.

C School of Biological Sciences, Monash University, Rainforest Walk, Melbourne, Vic. 3800, Australia.

D Corresponding author. Email: S.Verdon@latrobe.edu.au

Wildlife Research 48(5) 458-469 https://doi.org/10.1071/WR20133
Submitted: 6 August 2020  Accepted: 13 February 2021   Published: 16 April 2021

Journal Compilation © CSIRO 2021 Open Access CC BY

Abstract

Context: Species translocations are used in conservation globally. Although harvest for translocation may have negative impacts on source populations, translocation programs rarely explore ways of minimising those impacts. In fluctuating source populations, harvest timing may affect its impact because population size and trajectory vary among years.

Aims: We explored whether the timing and scale of harvest can be altered to reduce its impact on a fluctuating source population of Mallee Emu-wrens, Stipiturus mallee; an endangered passerine in south-eastern Australia. Mallee Emu-wren populations fluctuate with ~5–10-year drought–rain cycles.

Methods: We used population viability analysis (PVA) to compare the impact of five harvest scales (no harvest, 100, 200, 300 or 500 individuals) under three population trajectories (increasing, stable or decreasing) and two initial population sizes (our model-based estimate of the population size and the lower 95% confidence interval of that estimate). To generate a model-based estimate of the population size, we surveyed 540 sites (9 ha), stratified according to environmental variables known to affect Mallee Emu-wren occurrence. We used an information-theoretic approach with N-mixture models to estimate Mallee Emu-wren density, and extrapolated results over all potential habitat.

Key Results: We estimate that in spring 2019, the source population consisted of 6449 individuals, with a minimum of 1923 individuals (lower 95% confidence interval). Of 48 harvest scenarios, only seven showed no impact of harvest within 5 years (15%). Those seven all had increasing population trajectories and carrying capacity set to equal initial population size. Twenty-six populations showed no impact of harvest within 25 years (54%). These were either increasing populations that had reached carrying capacity or decreasing populations nearing extinction.

Conclusions: Initial population size, carrying capacity, harvest scale and population trajectory were all determinants of harvest impact. Given the importance of carrying capacity, further research is required to determine its role in the Mallee Emu-wren source population.

Implications: Harvesting Mallee Emu-wrens after high-rainfall years will have the least impact because source populations are likely to be large with increasing trajectories. For fluctuating source populations, flexibility in the timing of harvest can reduce its impact and should be considered during translocation planning.

Keywords: abundance, conservation management, conservation planning, endangered species, population modelling, population viability, population management, threatened species.


References

Akaike, H. (1974). A new look at the statistical model identification. IEEE Transactions on Automatic Control 19, 716–723.
A new look at the statistical model identification.Crossref | GoogleScholarGoogle Scholar |

Armstrong, D. P., and Reynolds, M. H. (2012). Modelling reintroduced populations: the state of the art and future directions. In ‘Reintroduction biology: integrating science and management’. (Eds Ewen, J. G., Armstrong, D. P., Parker, K. A. and P. J. Seddon.) pp. 165. (John Wiley & Sons.)

Berger-Tal, O., Blumstein, D. T., and Swaisgood, R. R. (2020). Conservation translocations: a review of common difficulties and promising directions. Animal Conservation 23, 121–131.
Conservation translocations: a review of common difficulties and promising directions.Crossref | GoogleScholarGoogle Scholar |

Bode, M., and Brennan, K. E. C. (2011). Using population viability analysis to guide research and conservation actions for Australia’s threatened malleefowl Leipoa ocellata. Oryx 45, 513–521.
Using population viability analysis to guide research and conservation actions for Australia’s threatened malleefowl Leipoa ocellata.Crossref | GoogleScholarGoogle Scholar |

Brook, B. W., and Bradshaw, C. J. (2006). Strength of evidence for density dependence in abundance time series of 1198 species. Ecology 87, 1445–1451.
Strength of evidence for density dependence in abundance time series of 1198 species.Crossref | GoogleScholarGoogle Scholar | 16869419PubMed |

Brown, S., Clarke, M. F., and Clarke, R. H. (2009). Fire is a key element in the landscape-scale habitat requirements and global population status of a threatened bird: the Mallee Emu-wren (Stipiturus mallee). Biological Conservation 142, 432–445.
Fire is a key element in the landscape-scale habitat requirements and global population status of a threatened bird: the Mallee Emu-wren (Stipiturus mallee).Crossref | GoogleScholarGoogle Scholar |

Brown, S., Harrisson, K. A., Clarke, R. H., Bennett, A. F., and Sunnucks, P. (2013). Limited population structure, genetic drift and bottlenecks characterise an endangered bird species in a dynamic, fire-prone ecosystem. PLoS One 8, e59732.
Limited population structure, genetic drift and bottlenecks characterise an endangered bird species in a dynamic, fire-prone ecosystem.Crossref | GoogleScholarGoogle Scholar | 24376814PubMed |

Burgman, M., and Possingham, H. (2000). Population viability analysis for conservation: the good, the bad and the undescribed. In ‘Population Viability Analysis for Conservation’. (Eds A. G. Young, G. M. Clarke, and D. Clarke.) pp. 97–112. (Cambridge University Press.)

Callister, K. E., Griffioen, P. A., Avitabile, S. C., Haslem, A., Kelly, L. T., Kenny, S. A., Nimmo, D. G., Farnsworth, L. M., Taylor, R. S., and Watson, S. J. (2016). Historical maps from modern images: using remote sensing to model and map century-long vegetation change in a fire-prone region. PLoS One 11, e0150808.
Historical maps from modern images: using remote sensing to model and map century-long vegetation change in a fire-prone region.Crossref | GoogleScholarGoogle Scholar | 27029046PubMed |

Céré, J., Vickery, W. L., and Dickman, C. R. (2015). Refugia and dispersal promote population persistence under variable arid conditions: a spatio-temporal simulation model. Ecosphere 6, 225.
Refugia and dispersal promote population persistence under variable arid conditions: a spatio-temporal simulation model.Crossref | GoogleScholarGoogle Scholar |

Clarke, R. H., Oliver, D. L., Boulton, R. L., Cassey, P., and Clarke, M. F. (2003). Assessing programs for monitoring threatened species; a tale of three honeyeaters (Meliphagidae). Wildlife Research 30, 427–435.
Assessing programs for monitoring threatened species; a tale of three honeyeaters (Meliphagidae).Crossref | GoogleScholarGoogle Scholar |

Clarke, M. F., Avitabile, S. C., Brown, L., Callister, K. E., Haslem, A., Holland, G. J., Kelly, L. T., Kenny, S. A., Nimmo, D. G., and Spence-Bailey, L. M. (2010). Ageing mallee eucalypt vegetation after fire: insights for successional trajectories in semi-arid mallee ecosystems. Australian Journal of Botany 58, 363–372.
Ageing mallee eucalypt vegetation after fire: insights for successional trajectories in semi-arid mallee ecosystems.Crossref | GoogleScholarGoogle Scholar |

Colomer, M. À., Oliva-Vidal, P., Jiménez, J., Martínez, J. M., and Margalida, A. (2020). Prioritizing among removal scenarios for the reintroduction of endangered species: insights from bearded vulture simulation modeling. Animal Conservation 23, 396–406.
Prioritizing among removal scenarios for the reintroduction of endangered species: insights from bearded vulture simulation modeling.Crossref | GoogleScholarGoogle Scholar |

Connell, J. (2019). Fire and Rain: Investigating how major ecological drivers shape a semi-arid bird community over space and time. Ph.D. Thesis, La Trobe University, Melbourne, Vic., Australia.

Dimond, W. J., and Armstrong, D. P. (2007). Adaptive harvesting of source populations for translocation: a case study with New Zealand robins. Conservation Biology 21, 114–124.
Adaptive harvesting of source populations for translocation: a case study with New Zealand robins.Crossref | GoogleScholarGoogle Scholar | 17298517PubMed |

Fiske, I., and Chandler, R. (2011). Unmarked: an R package for fitting hierarchical models of wildlife occurrence and abundance. Journal of Statistical Software 43, 1–23.
Unmarked: an R package for fitting hierarchical models of wildlife occurrence and abundance.Crossref | GoogleScholarGoogle Scholar |

Furlan, E. M., Gruber, B., Attard, C. R. M., Wager, R. N. E., Kerezsy, A., Faulks, L. K., Beheregaray, L. B., and Unmack, P. J. (2020). Assessing the benefits and risks of translocations in depauperate species: a theoretical framework with an empirical validation. Journal of Applied Ecology 57, 831–841.
Assessing the benefits and risks of translocations in depauperate species: a theoretical framework with an empirical validation.Crossref | GoogleScholarGoogle Scholar |

Garnett, S. T., and Geyle, H. M. (2018). The extent and adequacy of monitoring for Australian threatened bird species. In ‘Monitoring threatened species and Ecological Communities’. (Eds S. Legge, N. Robinson, D. Lindenmayer, B. Scheele, D. Southwell, and B. Wintle.) pp. 43–55. (CSIRO Publishing: Melbourne, Vic., Australia.)

Garnett, S. T., Szabo, J., and Dutson, G. (2011). ‘The action plan for Australian birds 2010.’ (CSIRO Publishing: Melbourne, Vic., Australia.)

Haslem, A., Callister, K. E., Avitabile, S. C., Griffioen, P. A., Kelly, L. T., Nimmo, D. G., Spence-Bailey, L. M., Taylor, R. S., Watson, S. J., and Brown, L. (2010). A framework for mapping vegetation over broad spatial extents: a technique to aid land management across jurisdictional boundaries. Landscape and Urban Planning 97, 296–305.
A framework for mapping vegetation over broad spatial extents: a technique to aid land management across jurisdictional boundaries.Crossref | GoogleScholarGoogle Scholar |

Higgins, P. J., Peter, J. M., and Steele, W. K. (Eds) (2001). ‘Handbook of Australian, New Zealand and Antarctic Birds. Vol. 5: Tyrant flycatchers to chats.’ (Oxford University Press: Melbourne, Vic., Australia.)

Hijmans, R. J., Van Etten, J., Cheng, J., Mattiuzzi, M., Sumner, M., Greenberg, J. A., Lamigueiro, O. P., Bevan, A., Racine, E. B., and Shortridge, A. (2015). ‘R Package ‘raster’’. Available at https://CRAN.R-project.org/package=raster [verified 22 March 2021].

Holmgren, M., Stapp, P., Dickman, C. R., Gracia, C., Graham, S., Gutiérrez, J. R., Hice, C., Jaksic, F., Kelt, D. A., Letnic, M., Lima, M., López, B. C., Meserve, P. L., Milstead, W. B., Polis, G. A., Previtali, M. A., Richter, M., Sabaté, S., and Squeo, F. A. (2006). Extreme climatic events shape arid and semiarid ecosystems. Frontiers in Ecology and the Environment 4, 87–95.
Extreme climatic events shape arid and semiarid ecosystems.Crossref | GoogleScholarGoogle Scholar |

IUCN (2013). ‘Guidelines for reintroductions and other conservation translocations.’ (IUCN Species Survival Commission: Gland, Switzerland.)

Kéry, M., and Royle, J. A. (2015). ‘Applied Hierarchical Modeling in Ecology: Analysis of distribution, abundance and species richness in R and BUGS: Vol. 1: Prelude and Static Models.’ (Academic Press.)

Knape, J., and de Valpine, P. (2012). Are patterns of density dependence in the Global Population Dynamics Database driven by uncertainty about population abundance? Ecology Letters 15, 17–23.
Are patterns of density dependence in the Global Population Dynamics Database driven by uncertainty about population abundance?Crossref | GoogleScholarGoogle Scholar | 22017744PubMed |

Lacy, R. C., and Pollak, J. P. (2020). ‘Vortex: a stochastic simulation of the extinction process. Version 10.3.8.’ (Chicago Zoological Society: Brookfield, IL, USA.)

Lande, R., Engen, S., and Saether, B.-E. (2003). ‘Stochastic population dynamics in ecology and conservation.’ (Oxford University Press.)

Letnic, M., and Dickman, C. R. (2006). Boom means bust: interactions between the El Niño/Southern Oscillation (ENSO), rainfall and the processes threatening mammal species in arid Australia. Biodiversity and Conservation 15, 3847–3880.
Boom means bust: interactions between the El Niño/Southern Oscillation (ENSO), rainfall and the processes threatening mammal species in arid Australia.Crossref | GoogleScholarGoogle Scholar |

Maguire, G. S. (2005). Behavioural ecology of the Southern Emu-wren (Stipiturus malachurus). Ph.D. Thesis, University of Melbourne, Melbourne, Vic., Australia.

Maguire, G. S. (2006). Territory quality, survival and reproductive success in southern emu‐wrens Stipiturus malachurus. Journal of Avian Biology 37, 579–593.

Maguire, G. S., and Mulder, R. A. (2004). Breeding biology and demography of the southern emu-wren (Stipiturus malachurus). Australian Journal of Zoology 52, 583–604.
Breeding biology and demography of the southern emu-wren (Stipiturus malachurus).Crossref | GoogleScholarGoogle Scholar |

Martin, T. G., Nally, S., Burbidge, A. A., Arnall, S., Garnett, S. T., Hayward, M. W., Lumsden, L. F., Menkhorst, P., McDonald‐Madden, E., and Possingham, H. P. (2012). Acting fast helps avoid extinction. Conservation Letters 5, 274–280.
Acting fast helps avoid extinction.Crossref | GoogleScholarGoogle Scholar |

Menkhorst, P., Rogers, D., Clarke, R. H., Davies, D., Marsack, P., and Franklin, K. (2017). ‘The Australian Bird Guide.’ (CSIRO Publishing: Melbourne, Vic., Australia.)

Miller, J. A. O., Furness, R. W., Trinder, M., and Matthiopoulos, J. (2019). The sensitivity of seabird populations to density-dependence, environmental stochasticity and anthropogenic mortality. Journal of Applied Ecology 56, 2118–2130.
The sensitivity of seabird populations to density-dependence, environmental stochasticity and anthropogenic mortality.Crossref | GoogleScholarGoogle Scholar |

Mitchell, W. F., Boulton, R. L., Ireland, L., Hunt, T. J., Verdon, S. J., Olds, L. G. M., Hedger, C., and Clarke, R. H. (2021). Using experimental trials to improve translocation protocols for a cryptic, endangered passerine. Pacific Conservation Biology , .
Using experimental trials to improve translocation protocols for a cryptic, endangered passerine.Crossref | GoogleScholarGoogle Scholar |

Paton, D. C., Rogers, D. J., Cale, P., Willoughby, N., and Gates, J. A. (2009). Chapter 14: Birds. In ‘Natural history of the Riverland and Murraylands’. (Ed. J. T. Jennings.) (Royal Society of South Australia: Adelaide, SA, Australia.)

Pérez, I., Anadón, J. D., Díaz, M., Nicola, G. G., Tella, J. L., and Giménez, A. (2012). What is wrong with current translocations? A review and a decision‐making proposal. Frontiers in Ecology and the Environment 10, 494–501.
What is wrong with current translocations? A review and a decision‐making proposal.Crossref | GoogleScholarGoogle Scholar |

R Core Team (2019). ‘R: A language and environment for statistical computing.’ (R Foundation for Statistical Computing: Vienna, Austria.)

Reed, J. M., Mills, L. S., Dunning, J. B., Menges, E. S., McKelvey, K. S., Frye, R., Beissinger, S. R., Anstett, M.-C., and Miller, P. (2002). Emerging issues in Population Viability Analysis. Conservation Biology 16, 7–19.
Emerging issues in Population Viability Analysis.Crossref | GoogleScholarGoogle Scholar |

Rowe, M., and Pruett-Jones, S. (2008). Reproductive anatomy of male southern emu-wrens (Stipiturus malachurus) and striated grasswrens (Amytornis striatus). Emu-Austral Ornithology 108, 68–73.
Reproductive anatomy of male southern emu-wrens (Stipiturus malachurus) and striated grasswrens (Amytornis striatus).Crossref | GoogleScholarGoogle Scholar |

Seddon, P. J., Armstrong, D. P., and Maloney, R. F. (2007). Developing the science of Reintroduction Biology. Conservation Biology 21, 303–312.
Developing the science of Reintroduction Biology.Crossref | GoogleScholarGoogle Scholar | 17391180PubMed |

Seddon, P. J., Griffiths, C. J., Soorae, P. S., and Armstrong, D. P. (2014). Reversing defaunation: restoring species in a changing world. Science 345, 406–412.
Reversing defaunation: restoring species in a changing world.Crossref | GoogleScholarGoogle Scholar | 25061203PubMed |

Southgate, R., and Possingham, H. (1995). Modelling the reintroduction of the greater bilby Macrotis lagotis using the metapopulation model Analysis of the Likelihood of Extinction (ALEX). Biological Conservation 73, 151–160.
Modelling the reintroduction of the greater bilby Macrotis lagotis using the metapopulation model Analysis of the Likelihood of Extinction (ALEX).Crossref | GoogleScholarGoogle Scholar |

Verdon, S. J., Watson, S. J., and Clarke, M. F. (2019). Modeling variability in the fire response of an endangered bird to improve fire‐management. Ecological Applications 29, e01980.
Modeling variability in the fire response of an endangered bird to improve fire‐management.Crossref | GoogleScholarGoogle Scholar |

Verdon, S. J., Watson, S. J., Nimmo, D. G., and Clarke, M. F. (2020). Are all fauna associated with the same structural features of the hummock-grass Triodia scariosa? Austral Ecology 45, 773–787.

White, M. D. (2006). The mallee vegetation of north western Victoria. Proceedings of the Royal Society of Victoria 118, 229–243.

Wolf, S., Hartl, B., Carroll, C., Neel, M. C., and Greenwald, D. N. (2015). Beyond PVA: why recovery under the Endangered Species Act is more than population viability. Bioscience 65, 200–207.
Beyond PVA: why recovery under the Endangered Species Act is more than population viability.Crossref | GoogleScholarGoogle Scholar |