School of BioSciences - Research Publications

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    Interactive effects of climate change and fire on metapopulation viability of a forest-dependent frog in south-eastern Australia
    Penman, TD ; Keith, DA ; Elith, J ; Mahony, MJ ; Tingley, R ; Baumgartner, JB ; Regan, TJ (ELSEVIER SCI LTD, 2015-10)
    Climate change directly affects the suitability of habitats for species, but also indirectly alters natural disturbances such as fire, which can negatively impact species’ persistence. Developing accurate predictions of climate change impacts requires estimates of the interactive effects of climate and disturbance regimes at both population and landscape scales. Here we couple a habitat suitability model with a population viability model to examine the interactive effects of climate change and altered fire regimes on a fire-responsive frog species across its geographic range in south-eastern Australia. By 2100, we predict expected minimum abundances (EMA) to decline by 66% (under GFDL-CM2 A1FI climate projections) or 87% (CSIRO Mk3.5 A1FI) in the absence of fire. Increased frequency of low-intensity fires reduced EMA by less than 5%, whereas increased frequency of high-intensity fires reduced EMA by up to 40% compared with the no-fire scenario. While shifts in fire regimes are predicted to impact metapopulation viability, these indirect effects of fire are far less severe than the direct impact of climate change on habitat suitability. Exploring the interactive impacts of climate change and altered disturbance regimes can help managers prioritize threats across space and time.
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    Is my species distribution model fit for purpose? Matching data and models to applications
    Guillera-Arroita, G ; Lahoz-Monfort, JJ ; Elith, J ; Gordon, A ; Kujala, H ; Lentini, PE ; McCarthy, MA ; Tingley, R ; Wintle, BA (WILEY, 2015-03)
    Abstract Species distribution models (SDMs) are used to inform a range of ecological, biogeographical and conservation applications. However, users often underestimate the strong links between data type, model output and suitability for end‐use. We synthesize current knowledge and provide a simple framework that summarizes how interactions between data type and the sampling process (i.e. imperfect detection and sampling bias) determine the quantity that is estimated by a SDM. We then draw upon the published literature and simulations to illustrate and evaluate the information needs of the most common ecological, biogeographical and conservation applications of SDM outputs. We find that, while predictions of models fitted to the most commonly available observational data (presence records) suffice for some applications, others require estimates of occurrence probabilities, which are unattainable without reliable absence records. Our literature review and simulations reveal that, while converting continuous SDM outputs into categories of assumed presence or absence is common practice, it is seldom clearly justified by the application's objective and it usually degrades inference. Matching SDMs to the needs of particular applications is critical to avoid poor scientific inference and management outcomes. This paper aims to help modellers and users assess whether their intended SDM outputs are indeed fit for purpose.
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    Predicting species distributions for conservation decisions
    Guisan, A ; Tingley, R ; Baumgartner, JB ; Naujokaitis-Lewis, I ; Sutcliffe, PR ; Tulloch, AIT ; Regan, TJ ; Brotons, L ; McDonald-Madden, E ; Mantyka-Pringle, C ; Martin, TG ; Rhodes, JR ; Maggini, R ; Setterfield, SA ; Elith, J ; Schwartz, MW ; Wintle, BA ; Broennimann, O ; Austin, M ; Ferrier, S ; Kearney, MR ; Possingham, HP ; Buckley, YM ; Arita, H (WILEY, 2013-12)
    Species distribution models (SDMs) are increasingly proposed to support conservation decision making. However, evidence of SDMs supporting solutions for on-ground conservation problems is still scarce in the scientific literature. Here, we show that successful examples exist but are still largely hidden in the grey literature, and thus less accessible for analysis and learning. Furthermore, the decision framework within which SDMs are used is rarely made explicit. Using case studies from biological invasions, identification of critical habitats, reserve selection and translocation of endangered species, we propose that SDMs may be tailored to suit a range of decision-making contexts when used within a structured and transparent decision-making process. To construct appropriate SDMs to more effectively guide conservation actions, modellers need to better understand the decision process, and decision makers need to provide feedback to modellers regarding the actual use of SDMs to support conservation decisions. This could be facilitated by individuals or institutions playing the role of 'translators' between modellers and decision makers. We encourage species distribution modellers to get involved in real decision-making processes that will benefit from their technical input; this strategy has the potential to better bridge theory and practice, and contribute to improve both scientific knowledge and conservation outcomes.