Amphibian fungal panzootic causes catastrophic and ongoing loss of biodiversity

Anthropogenic trade and development have broken down dispersal barriers, facilitating the spread of diseases that threaten Earth's biodiversity. We present a global, quantitative assessment of the amphibian chytridiomycosis panzootic, one of the most impactful examples of disease spread, and demonstrate its role in the decline of at least 501 amphibian species over the past half-century, including 90 presumed extinctions. The effects of chytridiomycosis have been greatest in large-bodied, range-restricted anurans in wet climates in the Americas and Australia. Declines peaked in the 1980s, and only 12% of declined species show signs of recovery, whereas 39% are experiencing ongoing decline. There is risk of further chytridiomycosis outbreaks in new areas. The chytridiomycosis panzootic represents the greatest recorded loss of biodiversity attributable to a disease

Is Chytridiomycosis an Emerging Infectious Disease in Asia?

The disease chytridiomycosis, caused by the fungus Batrachochytrium dendrobatidis (Bd), has caused dramatic amphibian population declines and extinctions in Australia, Central and North America, and Europe. Bd is associated with >200 species extinctions of amphibians, but not all species that become infected are susceptible to the disease. Specifically, Bd has rapidly emerged in some areas of the world, such as in Australia, USA, and throughout Central and South America, causing population and species collapse. The mechanism behind the rapid global emergence of the disease is poorly understood, in part due to an incomplete picture of the global distribution of Bd. At present, there is a considerable amount of geographic bias in survey effort for Bd, with Asia being the most neglected continent. To date, Bd surveys have been published for few Asian countries, and infected amphibians have been reported only from Indonesia, South Korea, China and Japan. Thus far, there have been no substantiated reports of enigmatic or suspected disease-caused population declines of the kind that has been attributed to Bd in other areas. In order to gain a more detailed picture of the distribution of Bd in Asia, we undertook a widespread, opportunistic survey of over 3,000 amphibians for Bd throughout Asia and adjoining Papua New Guinea. Survey sites spanned 15 countries, approximately 36° latitude, 111° longitude, and over 2000 m in elevation. Bd prevalence was very low throughout our survey area (2.35% overall) and infected animals were not clumped as would be expected in epizootic events. This suggests that Bd is either newly emerging in Asia, endemic at low prevalence, or that some other ecological factor is preventing Bd from fully invading Asian amphibians. The current observed pattern in Asia differs from that in many other parts of the world

Detection of Batrachochytrium dendrobatidis in amphibians imported into the UK for the pet trade

There is increasing evidence that the global spread of the fungal pathogen Batrachochytrium dendrobatidis (Bd) has been facilitated by the international trade in amphibians. Bd was first detected in the UK in 2004, and has since been detected in multiple wild amphibian populations. Most amphibians imported into the UK for the pet trade from outside the European Union enter the country via Heathrow Animal Reception Centre (HARC), where Bd positive animals have been previously detected. Data on the volume, diversity and origin of imported amphibians were collected for 59 consignments arriving at HARC between November 2009 and June 2012, along with a surveillance study to investigate the prevalence of Bd in these animals. Forty three amphibian genera were recorded, originating from 12 countries. It was estimated that 5000 – 7000 amphibians are imported through HARC into the UK annually for the pet trade. Bd was detected in consignments from the USA and Tanzania, in six genera, resulting in an overall prevalence of 3.6%. This suggests that imported amphibians are a source of Bd within the international pet trade

Amphibian pathogens in southeast asian frog trade

10.1007/s10393-013-0817-7EcoHealth94386-39

Cryptic diversity of a widespread global pathogen reveals expanded threats to amphibian conservation

Biodiversity loss is one major outcome of human-mediated ecosystem disturbance. One way that humans have triggered wildlife declines is by transporting disease-causing agents to remote areas of the world. Amphibians have been hit particularly hard by disease due in part to a globally distributed pathogenic chytrid fungus (Batrachochytrium dendrobatidis [Bd]). Prior research has revealed important insights into the biology and distribution of Bd; however, there are still many outstanding questions in this system. Although we know that there are multiple divergent lineages of Bd that differ in pathogenicity, we know little about how these lineages are distributed around the world and where lineages may be coming into contact. Here, we implement a custom genotyping method for a global set of Bd samples. This method is optimized to amplify and sequence degraded DNA from noninvasive skin swab samples. We describe a divergent lineage of Bd, which we call BdASIA3, that appears to be widespread in Southeast Asia. This lineage co-occurs with the global panzootic lineage (BdGPL) in multiple localities. Additionally, we shed light on the global distribution of BdGPL and highlight the expanded range of another lineage, BdCAPE. Finally, we argue that more monitoring needs to take place where Bd lineages are coming into contact and where we know little about Bd lineage diversity. Monitoring need not use expensive or difficult field techniques but can use archived swab samples to further explore the history-and predict the future impacts-of this devastating pathogen

Unraveling the historical prevalence of the invasive chytrid fungus in the Bolivian Andes: implications in recent amphibian declines

We studied the historical prevalence of the invasive and pathogenic chytrid fungus Batrachochytrium dendrobatidis (Bd) among amphibians from the Bolivian Andes. Our aim was also to determine its geographic pattern of dispersion, and a potential host taxonomic signature. We collected frog tissue samples from nine museum collections covering a period from 1863 to 2005 and from the field during 2009–2016. Bd was diagnosed via quantitative PCR in 599 individuals of 17 genera and 54 species. We found an overall Bd prevalence of 41% among 44 species tested. The first incidence of Bd was from a Telmatobius culeus in 1863; this is the earliest report of detection for this pathogen in the world. Results reveal a non-random historical and geographical pattern of Bd occurrence and amphibian declines that suggests the presence of two different invasive strains, an ancient endemic and a more recent introduction. Prevalence of Bd increased significantly by the mid-1990s, particularly in the cloud-forests, and this is coincident with the timing of drastic amphibian declines. In contrast, amphibians occurring in drier altiplano habitats have persisted in spite of Bd presence. We hypothesize that the early 1990s, and the cloud-forests in central Bolivia were the center of an epidemic surge of Bd that took its toll on many species, especially in the genus Telmatobius. Further sampling of cloud-forest species, and ongoing genetic studies of Bd isolates from Bolivia should help resolve the history of this invasive pathogen and test hypotheses on the differential response of endangered hosts.This research was supported by Projects CGL2011-30393 and CGL2014-56160-P of the Spanish Government (PI, Ignacio De la Riva).Peer Reviewe

Amphibian chytrid prevalence in an amphibian community in arid Australia

[Extract] The amphibian disease chytridiomycosis, caused by the pathogen Batrachochytrium dendrobatidis (Bd), has dramatically affected amphibians, causing population declines in over 200 species worldwide (Fisher et al. 2009). The disease is widespread, driving amphibian declines in North America (Muths et al. 2003; Briggs et al. 2005), Australia (Berger et al. 1998), Central America (Lips et al. 2006) and South America (Catenazzi et al. 2011). The variation in susceptibility to disease and mortality seen among host species, populations and locations is at least partially driven by interplay between external environmental and internal host-specific factors (Woodhams et al. 2007; Searle et al. 2011; Blaustein et al. 2012). While at a single location some species may be locally extirpated, others may persist (Lips et al. 2006). Amphibian infection prevalence and mortality rates due to chytridiomycosis are correlated with ambient environmental conditions: being highest during cooler months and at higher elevations (Berger et al. 1998; Woodhams and Alford 2005; Kriger and Hero 2008)