Limited Understanding of Bushfire Impacts on Australian Invertebrates
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Insect Conservation and Diversity (2021) doi: 10.1111/icad.12493 FORUM & POLICY Limited understanding of bushfire impacts on Australian invertebrates MANU E. SAUNDERS,1 PHILIP S. BARTON,1,2 JAMESR.M.BICKERSTAFF,3 LINDSEY FROST,1 TANYA LATTY,4 BRYAN D. LESSARD,5 ELIZABETH C. LOWE,6 JUANITA RODRIGUEZ,5 THOMAS E. WHITE4 and 3,7 KATE D. L. UMBERS 1School of Environmental and Rural Sciences, University of New England, Armidale, NSW, Australia, 2School of Science, Psychology and Sport, Federation University Australia, Mount Helen, VC, Australia, 3Hawkesbury Institute for the Environment, Western Sydney University, Penrith, NSW, Australia, 4School of Life and Environmental Sciences, University of Sydney, Sydney, NSW, Australia, 5Australian National Insect Collection, CSIRO, Canberra, ACT, Australia, 6Department of Biological Sciences, Macquarie University, Sydney, NSW, Australia and 7School of Science, Western Sydney University, Penrith, NSW, Australia Abstract. 1. Understanding how increasing risk of frequent and severe fires affects biodiversity and ecosystem function is important for effective conservation and recovery, but large knowledge gaps exist for many taxa in many parts of the world, especially invertebrates. 2. After Australia’s 2019–2020 catastrophic bushfire disaster, estimates of biodiver- sity loss and government priorities for post-fire conservation activities were focused on vertebrates and plants because of lack of knowledge about invertebrates. 3. Our synthesis of published evidence reveals a fragmented and ambiguous body of literature on invertebrate responses to fire in Australian ecosystems, limiting the capacity of evidence to inform effective conservation policy in response to extreme fire events. Peer-reviewed studies are available for only six of the more than 30 invertebrate phyla and 88% were on arthropods, predominantly ants. 4. Nearly all studies (94%) were conducted in terrestrial habitats, with only four stud- ies measuring impacts in freshwater habitats and no studies of impacts on marine inver- tebrates. The high variation in study designs and treatment categories, as well as the absence of key methodological details in many older observational studies, means that there is substantial opportunity to improve our approach to collating meaningful esti- mates of general fire effects. 5. To understand the full ecological effects of catastrophic fire events, and design effective policies that support recovery of ecosystems now and in future, it is critical that we improve understanding of how fire regimes affect invertebrates. We list key priorities for research and policy to support invertebrate conservation and ecosystem recovery in the face of increasing fire risk. Key words. Biodiversity, ecosystem function, ecosystem recovery, fire, insects, mega- fire, wildfire. Introduction Global climate change is increasing the risk of frequent, severe fires around the world (Virgilio et al., 2019; Goss et al., 2020). fi Correspondence: Manu E. Saunders, School of Environmental and Understanding how res affect biodiversity is important for Rural Sciences, University of New England, Armidale, NSW 2350, effective conservation and recovery efforts, but there are signif- Australia. E-mail: [email protected] icant gaps in our understanding of the taxa most at risk in many © 2021 Royal Entomological Society. 1 2 Manu E. Saunders et al. parts of the world (Driscoll et al., 2010). This is particularly true contrast, there is little understanding of how the fire season for invertebrates, which include a staggering diversity of species affected Australia’s unique invertebrate fauna because funda- with more than 1 million known to science (Roskov et al., 2020), mental baseline data have not been collected in most places for and an estimated 4 million undiscovered or undescribed most taxa. Failure to systematically collect monitoring data has (Stork, 2018). The majority of invertebrate species are critical left us with no meaningful ways to assess the impact of the fires to ecosystem function and associated ecosystem services across on our invertebrate fauna and therefore severely limits our under- all biomes and in managed and unmanaged systems standing of how critical ecosystem functions have been impacted (Wallace & Webster, 1996; Boulton et al., 2008; Prather and which recovery activities should be prioritised. et al., 2013; Yang & Gratton, 2014; Saunders, 2018). Paradoxi- Catastrophic fire events, which are predicted to become more cally, they are also the most understudied group of animals and frequent and severe in Australia based on recent modelled climate large knowledge gaps about invertebrate identification, ecology change scenarios (Dowdy et al., 2019), have the potential to signif- and distribution limit our understanding of their responses to sto- icantly restructure ecological communities, cause local extinctions, chastic events and environmental change (Cardoso et al., 2011). and disrupt ecological interactions that are essential to ecosystem In Australia, only about 30% of the invertebrate fauna (over recovery. The paucity of data on invertebrates leaves us with no 320 000 species) has been described (Braby, 2018). Due to a lack guidelines for protecting invertebrate species in the face of increas- of baseline knowledge for the majority of species, a very small ing prevalence and risk of future bushfires. Australia’s megafires proportion (653 species) are listed as threatened under state and captured global attention and millions of dollars were donated to Commonwealth legislation and the International Union for Con- bushfire recovery efforts, leaving many agencies with the question servation of Nature’s Red List, the vast majority of which are land of what to prioritise. Post-fire government priorities for conserva- snails (Stylommatophora), crayfish (Decapoda), and butterflies tion funding targeted individual species comprising approximately and moths (Lepidoptera). Although threatened species lists are 0.06% of Australia’s invertebrate diversity compared to about intended as a tool to prioritise conservation funding and action, 1.2% of Australia’s vertebrates and about 1.9% of plants such lists currently cannot account for undescribed species with (Woinarski et al., 2020b). Listing was based on species captured unknown roles in the ecosystem until they are formally documen- in current threatened species legislation, by distribution mapping ted and recognised by science. This means that when mounting a and/or collated via expert advice (Woinarski et al., 2020b). This priority-based response to catastrophic disasters, unlisted species approach unfortunately misses the larger majority of unstudied and, moreover, unknown species, can easily be ignored. The and undescribed species impacted by the fires and it is possible that implications of this dearth of knowledge became apparent during many undescribed species may now be at risk. For example, in Australia’s recent catastrophic bushfire disaster. From August recent months, several new invertebrate specimens collected 2019 to February 2020, fires burned continuously through more before the fires from fire-impacted areas have been formally than 10 million hectares (approx. 25 million acres), over 80% described as species new to science (Lessard et al., 2020; Yuan & of this area native forests, until the last fires were extinguished Rodriguez, 2020). This is likely to be a growing trend as more by heavy rainfall (Davey & Sarre, 2020). Multiple bioregions invertebrates in the estimated 70% of unknown species continue and ecosystem types were affected, including many unique to be described from museum collections. In the meantime, current Australian forests and threatened ecological communities, such policy and decision-making to facilitate immediate and medium- as the World Heritage listed Gondwana Rainforests and Greater term responses to fire recovery is informed by a body of knowledge Blue Mountains area, grassy woodlands, alpine grasslands and that largely excludes invertebrate ecology and life histories, and meadows, and temperate rainforest (Boer et al., 2020; Kooyman could result in poor biodiversity recovery outcomes. It is unreason- et al., 2020; Lindenmayer & Taylor, 2020). able to expect rapid expansion of invertebrate threatened species Although Australia is a fire-prone country, the unprecedented lists to counter this, due to knowledge limitations and the need spatial and temporal scale of this fire season, and the intensity for formal taxonomic descriptions. A more immediate solution is and severity of many of the burns, were unlike anything scien- to focus policy and restoration efforts on ecosystems and commu- tists and firefighting experts had experienced before (Boer nities, rather than species, to limit the potential bias of decisions et al., 2020; Nolan et al., 2020). The catastrophic event captured informed by vertebrate ecology and distributions. global attention, especially as smoke from the fires made a full In this commentary, we seek to amplify the discourse on how fire circuit around the globe affecting air quality and depositing aero- impacts biodiversity and increase focus on the neglected yet domi- sols in other countries including New Zealand and on the South nant group of animals that drive ecosystem function and influence American continent (Seftor & Gutro, 2020). The fire event ecosystem recovery. We focus on Australia, the core of our exper- turned the spotlight on what we know, and do not know, about tise, because the 2019–2020 Australian megafires were