ReviewAfter the epidemic: Ongoing declines, stabilizations and recoveries in amphibians afflicted by chytridiomycosis
Introduction
Wildlife disease is implicated as a key driver of species extinction (e.g. Daszak et al., 2000, Fisher et al., 2012). In the past decade, disease-driven mass declines have been reported across many groups, including amphibians, reptiles, birds, mammals, fishes and corals (Fisher et al., 2012, Lorch et al., 2015, Tompkins et al., 2015). Immediate effects of outbreaks due to pathogen emergence in naïve wildlife populations can be severe and overt (e.g. Blehert et al., 2009). In contrast, long-term disease impacts are more complex, dynamic and much harder to detect and assess. This is especially true when field studies have been initiated decades after the emergence of the pathogen, and pre-arrival records are lacking, such as for avian malaria (Plasmodium relictum) in Hawaiian birds (van Riper et al., 1986) and big-horn sheep pneumonia (Mycoplasma ovipneumoniae) in the Rocky Mountains (Besser et al., 2013). Host-pathogen coevolution theory postulates that a shift from epidemic to endemic states is generally associated with reduced pathogenicity, underpinned by increased host tolerance, resistance and/or reduced pathogen virulence (de Castro and Bolker, 2005). However, whether such shifts apply to generalist pathogens currently impacting biodiversity is uncertain. Generalist pathogens commonly persist in biotic reservoirs, potentially maintaining high disease impact in a sub-set of highly susceptible host species (de Castro and Bolker, 2005). As recently emerged pathogens become endemic in their new hosts and ranges, understanding the threat associated with ongoing pathogen presence is crucial for assessing impacts and informing conservation actions.
One of the most devastating diseases impacting wildlife over recent decades is amphibian chytridiomycosis, caused by the fungal skin pathogen Batrachochytrium dendrobatidis (‘Bd’) (Berger et al., 1998). Since its discovery, chytridiomycosis has been implicated in the decline of > 200 amphibian species, with declines attributed to the pathogen beginning in the 1970s (Skerratt et al., 2007). Bd infection has been reported in > 500 amphibian species (Olson et al., 2013) and although the origin of Bd remains unresolved (Rosenblum et al., 2013), it appears to be present in most climatically suitable regions worldwide (Olson et al., 2013).
The introduction of Bd into susceptible, naïve amphibian populations is characterized by a rapid, simultaneous increase in prevalence and infection intensity, followed by mass mortality and population decline (Lips et al., 2006, Vredenburg et al., 2010). If some individuals survive the initial epidemic, Bd may persist as an endemic pathogen in remnant populations or in resistant species that did not decline (Briggs et al., 2010, Murray et al., 2009, Reeder et al., 2012). Host impacts associated with endemic Bd are variable, with some species experiencing substantial ongoing mortality (Murray et al., 2009, Pilliod et al., 2010, Scheele et al., 2016b), which suppresses population abundance, while other species are stabilizing or beginning to recover (Newell et al., 2013, Scheele et al., 2015b). These variable host responses mean that the long-term threat associated with Bd remains uncertain across many parts of the globe.
Here, we investigate long-term host responses to Bd and mechanisms that influence Bd dynamics in declined species. First, using a continental-scale assessment of Australian amphibians, we review the impacts of chytridiomycosis 37 years post-Bd emergence. We categorize impacted species based on severity of decline, ongoing disease impact and whether population recovery has been observed. Chytridiomycosis was first reported in 1998 in Australia (Berger et al., 1998) and has subsequently been extensively studied across a large number of host species and environmental and climatic conditions (Berger et al., 2016). Recent reviews have focused on identifying actions, research and resources needed to prevent extinctions in threatened Australian frogs (Skerratt et al., 2016) and overviewed the taxonomy, phylogeny, distribution and ecology of Bd (Berger et al., 2016). However, a comprehensive assessment of Bd impacts and long-term population trajectories has not been undertaken, for Australia or other countries. We also review mechanisms and processes that influence endemic Bd dynamics across the globe to better understand factors underlying initial and ongoing disease impacts, incorporating case-studies of Australian species. Our focus on long-term host responses provides new insights into Bd impacts several decades post-emergence, and identifies the processes underlying variable host responses.
Section snippets
Chytridiomycosis in Australia: past and present
Some of the earliest reports of enigmatic amphibian declines globally were from eastern Australia, with disappearances of rainforest species first documented in 1979 (Skerratt et al., 2007). Over the following decades dramatic declines were reported in other tropical and temperate species in eastern Australia (Laurance et al., 1996, Osborne, 1989). The unprecedented decline of multiple species across geographic regions and an initial lack of a causal mechanism resulted in considerable debate on
Methods
We collated peer-reviewed articles, government technical reports, theses, conference proceedings, and unpublished data on species' status and trends recorded by amphibian ecologists and managers. Our research builds on and underpins the recommendations from the workshop described in Skerratt et al. (2016), which focused on prioritizing management for threatened Australian amphibian species impacted by chytridiomycosis. Literature was searched through Google Scholar and ISI Web of Knowledge,
Perspectives on amphibian conservation and Bd impacts in Australia
Our continent-scale assessment of chytridiomycosis impacts in Australia reveals that the disease is likely to have caused the extinction of seven species and contributed to the decline of a further 36 species since 1970. These declines represent nearly one fifth of the Australian amphibian fauna (238 species). In contrast, no amphibian extinctions were recorded in Australia from the time of European settlement in 1788 until 1970 (Hero et al., 2006, Hero and Morrison, 2004); a period that was
Mechanisms and processes influencing endemic Bd impacts globally
The ongoing, long-term impact associated with Bd is highly variable among species. Endemic Bd dynamics are influenced by a diverse range of factors operating at the pathogen, individual, and population levels (Fig. 4). Below we focus on mechanisms and processes underlying differential long-term responses to Bd presence. Understanding processes that influence Bd-host dynamics and host population persistence is crucial for refining our theoretical understanding of generalist host-pathogen
Conclusions
Batrachochytrium dendrobatidis is now approaching endemism in many regions of the world where it has been associated with declines (Murray et al., 2009, Muths et al., 2011, Olson et al., 2013). Our assessment of the trajectory of Australian amphibians afflicted by Bd illustrates that long-term impacts are highly variable. Nearly four decades post-emergence, some species are apparently stable and others are recovering, while several species are in an ongoing state of decline. We found that rapid
Acknowledgements
This paper is dedicated to Rick Speare and Keith McDonald whose efforts to understand the cause of amphibian declines in Queensland, Australia led to the discovery of chytridiomycosis. We acknowledge the enormous survey and monitoring efforts by Australian herpetologists over the past four decades. This study was funded by Australian Research Council grants (FT100100375, LP110200240 and DP120100811), a Queensland Accelerate Fellowship (14-218), NSW Office of Environment and Heritage, Queensland
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2022, Biological ConservationCitation Excerpt :There has been wide variability in population decline and response rates to Bd in enzootic systems, with some species increasing in population size and others remaining low (Catenazzi et al., 2017; Lampo et al., 2017). Decreased pathogen virulence has not been demonstrated in natural systems (Scheele et al., 2017b). Yet, some Atelopus populations in Central America are persisting in regions where Bd is detected (Perez et al., 2014).