A cryptic elapid snake persists in thewake of catastrophic wildfires
MIT C H E L L J. HODGSO N * 1 , 2 , 3 ,ALEXAND RA K. ROS S 2 , 3 , 4 ,YIN G Y O D LAPWONG5 , 6 SANTIAGO CUARTA S 5,BRI D G ET ROBE R TS 7,OWEN P RICE 7 ,JONA T H A N WEB B 5
NICOLA S EN TI NE LL A 2 , 3 ,J OSHUA L EE 2 , 3 ,SHAWN W. L AFF A N 8,HUGH M. BURLEY 8 F INLA Y MC I NTO S H 8 and MIKE L ETN I C 2
Abstract The increased severity and frequency of bushfires accompanying human-induced global warming have dire implications for biodiversity conservation. Herewe investigate the response of a cryptic, cool-climate elapid, the mustard- bellied snake Drysdalia rhodogaster,tothe extensiveBlack Summer fires of 2019/2020 in south-eastern Australia. The species is categorized as Least Concern on the IUCN Red List (last assessed in 2017), butbecausealarge partofits range was burnt during the Black Summer and little was known about its ecology, D. rhodogaster was identified as a priority species for post-fire impact assessment. We evaluated three lines of evidence to assess the impact of the Black Summer fires on D. rhodogaster. Habitat suitability modelling indicated that c. 46%of the predictedrange of the species was affected by bushfire. Field surveys conducted 9–36 months post-fire and collation of records from public databases submitted 0–24 months post-fire indicated that D. rhodogaster persisted in burnt landscapes. Fire severity and proportion of the landscape that was burnt within a 1,000-m radius of survey sites were poor predictors of site occupancy by D.
rhodogaster.Although conclusions regarding theeffectsoffireon D. rhodogaster are limited because of the lack of baseline data, it is evident that the species has persisted across the landscape in the wake of extensive bushfires. Our work highlights the need for baseline knowledge on cryptic species even when they are categorized as Least Concern, as otherwise assessments of the impacts of catastrophic events will be constrained.
*Corresponding author,
mitchell.hodgson@sydney.edu.au 1School of Life and Environmental Sciences, University of Sydney, Sydney,
Australia 2Evolution & Ecology Research Centre, School of Biological, Earth and
Environmental Sciences, University of New SouthWales, Sydney, Australia 3Centre for Ecosystem Science, School of Biological, Earth and Environmental
Sciences, University of New South Wales, Sydney, Australia 4Australian Wildlife Conservancy Yookamurra Wildlife Sanctuary, Fisher,
Australia 5School of Life Sciences, Faculty of Science, University of Technology Sydney,
Sydney, Australia 6Division of Biological Science, Faculty of Science, Prince of Songkla University,
Hat Yai, Thailand 7University of Wollongong, School of Earth, Atmosphere and Life Sciences,
Wollongong, Australia 8Earth and Sustainability Science Research Centre, School of Biological, Earth and Environmental Sciences, University of New South Wales, Sydney, Australia
Received 19 April 2023. Revision requested 13 June 2023. Accepted 5 January 2024. First published online 22 November 2024.
Keywords Black Summer, bushfire, Drysdalia rhodogaster, habitat suitability model, mustard-bellied snake, occupancy, reptile, species distribution
The supplementary material for this article is available at
doi.org/10.1017/S0030605324000048
Introduction
2009) and is crucial in maintaining the health of many eco- systems. Yet wildfires can lead to long-lasting changes in ecosystem structure, species distributions and species per- sistence (Haslem et al., 2011; Lovich et al., 2017; Merrick et al., 2021; Smith et al., 2021). At a regional scale, the extent, frequency and severity of fires can shift because of land-use changes such as human settlement (Spyratos et al., 2007) and logging (Lindenmayer et al., 2020). At a global scale, human-induced global warming is driving shifts in fire regimes, with forecasts and correlative studies predicting increases in the extent, frequency and severity of wildfires (Pitman et al., 2007; Canadell et al., 2021; van Oldenborgh et al., 2021). This increased prevalence of megafires has resulted in some authors referring to the contemporary period as the Pyrocene (Nimmo et al., 2021). Determining how different fire regimes directly and
F
indirectly affect species is a central research priority in contemporary conservation science (Driscoll et al., 2010). Although species in fire-prone landscapes have probably adapted to cope with the effects of fires, increased severity and frequency of fires could exceed the capacity of these adaptations to facilitate population persistence (Pausas & Parr, 2018; Nimmo et al., 2021). For example, in a fire- adapted landscape, a survey conducted 20 years after an extreme fire found only 7.9%of 1,630 shrubs showed any resprouting (Nicholson et al., 2017). Beyond direct mortal- ity, fire can have species-specific effects on habitat structure (Costa et al., 2020), fecundity (Smith et al., 2012) and preda- tion pressure (Leahy et al., 2016) that can cause shifts in eco- system dynamics. Because these effects are species-specific, comprehensive information across a range of taxa is re- quired to obtain a clear understanding of how ecosystems
This is an Open Access article, distributed under the terms of the Creative Commons Attribution licence (
http://creativecommons.org/licenses/by/4.0/), which permits unrestricted re-use, distribution and reproduction, provided the original article is properly cited. Oryx, 2024, 58(6), 769–778 © The Author(s), 2024. Published by Cambridge University Press on behalf of Fauna & Flora International doi:10.1017/S0030605324000048
ire is a natural process that has shaped landscapes glo- bally for more than 420 million years (Bowman et al.,
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