A DNA-based assay identifies Batrachochytrium dendrobatidis in amphibians

Chytridiomycosis caused by Batrachochytrium dendrobatidis (Chytridiomycota) has been implicated in declines of amphibian populations on four continents. We have developed a sensitive and specific polymerase chain reaction-based assay to detect this pathogen. We isolated B. dendrobatidis from captive and wild amphibians collected across North America and sequenced the internal transcribed spacer regions of the rDNA cassette of multiple isolates. We identified two primers (Bd1a and Bd2a) that are specific to B. dendrobatidis under amplification conditions described in this study. DNA amplification with Bd1a/Bd2a primers produced a fragment of approximately 300 bp from B. dendrobatidis DNA but not from DNA of other species of chytrids or common soil fungi. The assay detected 10 zoospores or 10 pg of DNA from B. dendrobatidis and detected infections in skin samples from a tiger salamander (Ambystoma tigrinum), boreal toads (Bufo boreas), Wyoming toads (Bufo baxteri), and smooth-sided toads (Bufo guttatus). This assay required only small samples of skin and can be used to process a large number of samples.     

Cryo-archiving of Batrachochytrium dendrobatidis and other chytridiomycetes

Batrachochytrium dendrobatidis is a major pathogen of frogs worldwide. It has been associated with catastrophic declines of frog populations including those in pristine habitats in Queensland, Australia. To facilitate genetic and disease studies of this fungus and related species, it is essential to have a reliable long-term storage method to maintain genetic integrity of isolates. We have adapted well-established techniques used for the long-term storage of tissue-culture cell lines to the preservation of B. dendrobatidis and other chytridiomycetes. This simple method has allowed us to recover these fungi from storage at -80 degrees C and in liquid nitrogen over an extended period. With this technique it is now possible to preserve saprobic and parasitic isolates from a variety of environmental and disease situations for comparative genetic and biological studies.     

Predicted disease susceptibility in a Panamanian amphibian assemblage based on skin peptide defenses

Chytridiomycosis is an emerging infectious disease of amphibians caused by a chytrid fungus, Batrachochytrium dendrobatidis. This panzootic does not equally affect all amphibian species within an assemblage; some populations decline, others persist. Little is known about the factors that affect disease resistance. Differences in behavior, life history, biogeography, or immune function may impact survival. We found that an innate immune defense, antimicrobial skin peptides, varied significantly among species within a rainforest stream amphibian assemblage that has not been exposed to B. dendrobatidis. If exposed, all amphibian species at this central Panamanian site are at risk of population declines. In vitro pathogen growth inhibition by peptides from Panamanian species compared with species with known resistance (Rana pipiens and Xenopus laevis) or susceptibility (Bufo boreas) suggests that of the nine species examined, two species (Centrolene prosoblepon and Phyllomedusa lemur) may demonstrate strong resistance, and the other species will have a higher risk of disease-associated population declines. We found little variation among geographically distinct B. dendrobatidis isolates in sensitivity to an amphibian skin peptide mixture. This supports the hypothesis that B. dendrobatidis is a generalist pathogen and that species possessing an innate immunologic defense at the time of disease emergence are more likely to survive.     

Possible modes of dissemination of the amphibian chytrid Batrachochytrium dendrobatidis in the environment

Amphibian chytridiomycosis caused by Batrachochytrium dendrobatidis has spread at an alarming rate over large distances throughout sensitive frog populations in eastern Australia, Central America and New Zealand. Infected amphibians and contaminated water are implicated in translocation, but other vectors are unknown. Through in vitro studies we show that potential means of translocation may be moist soil and bird feathers. B. dendrobatidis survived for up to 3 mo in sterile, moist river sand with no other nutrients added. B. dendrobatidis attached to and grew on sterile feathers and were able to be transported by feathers to establish new cultures in media, surviving between 1 and 3 h of drying between transfers. If these in vitro results are valid in the natural environment, the findings raise the possibilities that B. dendrobatidis may be translocated by movement of moist river sand and that birds may carry the amphibian chytrid between frog habitats. However, further studies using sand and feathers containing normal microflora are essential.     

Waterfowl: potential environmental reservoirs of the chytrid fungus Batrachochytrium dendrobatidis

Infections with Batrachochytrium dendrobatidis (B. dendrobatidis), the causal agent of chytridiomycosis, have been shown to play an important role in the decline of amphibians worldwide. Spread of the fungus is poorly understood. Bird movement might possibly contribute to the spread of B. dendrobatidis in the environment. Therefore, 397 wild geese in Belgium were screened for presence of B. dendrobatidis on their toes using real-time quantitative PCR (qPCR). In addition, chemotaxis towards, adhesion, survival after desiccation and proliferation of B. dendrobatidis on keratinous toe scales from waterfowl were examined in vitro. qPCR revealed that 76 geese (15%) were positive for B. dendrobatidis. Results of the in vitro tests showed that B. dendrobatidis is attracted to the keratinous toes of aquatic birds on which they can adhere and even proliferate. However, desiccation is poorly tolerated. This suggests waterfowl are potential environmental reservoirs for B. dendrobatidis.     

Survey for the pathogenic chytrid fungus Batrachochytrium dendrobatidis in southwestern North Carolina salamander populations

Batrachochytrium dendrobatidis is a fungal pathogen responsible for a potentially fatal disease of amphibians. We conducted a survey for B. dendrobatidis in the Appalachian Mountains of southwestern North Carolina, USA, from 10 June to 23 July 23 2009. Ventral skin swabs were collected from plethodontid salamanders (n=278) and real-time PCR was performed to test for the presence of B. dendrobatidis. We found no evidence of B. dendrobatidis, suggesting that B. dendrobatidis is absent or present in such low levels that it was undetected. If B. dendrobatidis was present at the time of our sampling, this survey supports evidence of low prevalence of B. dendrobatidis in North American headwater stream salamander populations.     

Fungicidal effects of chemical disinfectants, UV light, desiccation and heat on the amphibian chytrid Batrachochytrium dendrobatidis

The efficacy of a number of disinfection treatments was tested on in vitro cultures of the fungus Batrachochytrium dendrobatidis, the causative agent of chytridiomycosis in amphibians. The aim was to evaluate the fungicidal effects of chemical disinfectants, sterilising ultraviolet (UV) light, heat and desiccation, using methods that were feasible for either disinfection in the field, in amphibian husbandry or in the laboratory. The chemical disinfectants tested were: sodium chloride, household bleach (active ingredient: sodium hypochlorite), potassium permanganate, formaldehyde solution, Path-X agricultural disinfectant (active ingredient: didecyl dimethyl ammonium chloride, DDAC), quaternary ammonium compound 128 (DDAC), Dithane, Virkon, ethanol and benzalkonium chloride. In 2 series of experiments using separate isolates of B. dendrobatidis, the fungicidal effect was evaluated for various time periods and at a range of chemical concentrations. The end point measured was death of 100% of zoospores and zoosporangia. Nearly all chemical disinfectants resulted in 100%, mortality for at least one of the concentrations tested. However, concentration and time of exposure was critical for most chemicals. Exposure to 70% ethanol, 1 mg Virkon ml(-1) or 1 mg benzalkonium chloride ml(-1) resulted in death of all zoosporangia after 20 s. The most effective products for field use were Path-X and the quaternary ammonium compound 128, which can be used at dilutions containing low levels (e.g. 0.012 or 0.008%, respectively) of the active compound didecyl dimethyl ammonium chloride. Bleach, containing the active ingredient sodium hypochlorite, was effective at concentrations of 1% sodium hypochlorite and above. Cultures did not survive complete drying, which occurred after <3 h at room temperature. B. dendrobatidis was sensitive to heating, and within 4 h at 37 degrees C, 30 min at 47 degrees C and 5 min at 60 degrees C, 100% mortality occurred. UV light (at 1000 mW m(-2) with a wavelength of 254 nm) was ineffective at killing B. dendrobatidis in culture.     

Persistence of the emerging pathogen Batrachochytrium dendrobatidis outside the amphibian host greatly increases the probability of host extinction

Pathogens do not normally drive their hosts to extinction; however, Batrachochytrium dendrobatidis, which causes amphibian chytridiomycosis, has been able to do so. Theory predicts that extinction can be caused by long-lived or saprobic free-living stages. The hypothesis that such a stage occurs in B. dendrobatidis is supported by the recent discovery of an apparently encysted form of the pathogen. To investigate the effect of a free-living stage of B. dendrobatidis on host population dynamics, a mathematical model was developed to describe the introduction of chytridiomycosis into a breeding population of Bufo bufo, parametrized from laboratory infection and transmission experiments. The model predicted that the longer that B. dendrobatidis was able to persist in water, either due to an increased zoospore lifespan or saprobic reproduction, the more likely it was that it could cause local B. bufo extinction (defined as decrease below a threshold level). Establishment of endemic B. dendrobatidis infection in B. bufo, with severe host population depression, was also possible, in agreement with field observations. Although this model is able to predict clear trends, more precise predictions will only be possible when the life history of B. dendrobatidis, including free-living stages of the life cycle, is better understood.     

Environmental detection of Batrachochytrium dendrobatidis in a temperate climate

The aetiological agent of amphibian chytridiomycosis Batrachochytrium dendrobatidis is a primary cause of amphibian population declines. Current surveillance is based on the detection of B. dendrobatidis in its host but in vitro work suggests infective stages may survive in the abiotic environment for at least 3 mo. We describe here a surveillance system using filtration and quantitative PCR that can detect B. dendrobatidis in small (< 1 l) volumes of water. After assessing the analytical sensitivity of the protocol for both water and sediment samples in the laboratory, we analyzed environmental samples from the Sierra de Guadarrama mountain range in Spain at locations associated with chytrid-related die-offs and at other sites across Spain. B. dendrobatidis was detected in samples from 64% of the ponds in the Sierra de Guadarrama and at 2 sites outside this region, showing that levels of amphibian exposure to B. dendrobatidis are spatially heterogeneous. In experimental microcosms, we detected B. dendrobatidis for up to 12 wk, though we found no evidence for an overall increase in biomass. Our results emphasise the need to further investigate the life cycle of B. dendrobatidis to more completely understand the epidemiology of this emerging pathogen.     

Reptiles as potential vectors and hosts of the amphibian pathogen Batrachochytrium dendrobatidis in Panama

Chytridiomycosis, the disease caused by Batrachochytrium dendrobatidis, is considered to be a disease exclusively of amphibians. However, B. dendrobatidis may also be capable of persisting in the environment, and non-amphibian vectors or hosts may contribute to disease transmission. Reptiles living in close proximity to amphibians and sharing similar ecological traits could serve as vectors or reservoir hosts for B. dendrobatidis, harbouring the organism on their skin without succumbing to disease. We surveyed for the presence of B. dendrobatidis DNA among 211 lizards and 8 snakes at 8 sites at varying elevations in Panama where the syntopic amphibians were at pre-epizootic, epizootic or post-epizootic stages of chytridiomycosis. Detection of B. dendrobatidis DNA was done using qPCR analysis. Evidence of the amphibian pathogen was present at varying intensities in 29 of 79 examined Anolis humilis lizards (32%) and 9 of 101 A. lionotus lizards (9%), and in one individual each of the snakes Pliocercus euryzonus, Imantodes cenchoa, and Nothopsis rugosus. In general, B. dendrobatidis DNA prevalence among reptiles was positively correlated with the infection prevalence among co-occurring anuran amphibians at any particular site (r = 0.88, p = 0.004). These reptiles, therefore, may likely be vectors or reservoir hosts for B. dendrobatidis and could serve as disease transmission agents. Although there is no evidence of B. dendrobatidis disease-induced declines in reptiles, cases of coincidence of reptile and amphibian declines suggest this potentiality. Our study is the first to provide evidence of non-amphibian carriers for B. dendrobatidis in a natural Neotropical environment.     

Sodium hypochlorite denatures the DNA of the amphibian chytrid fungus Batrachochytrium dendrobatidis

Batrachochytrium dendrobatidis, an aquatic amphibian fungus, has been implicated in many amphibian declines and extinctions. A real-time polymerase chain reaction (PCR) TaqMan assay is now used to detect and quantify B. dendrobatidis on amphibians and other substrates via tissue samples, swabbing and filtration. The extreme sensitivity of this diagnostic test makes it necessary to rigorously avoid cross-contamination of samples, which can produce false positives. One technique used to eliminate contamination is to destroy the contaminating DNA by chemical means. We tested 3 concentrations of sodium hypochlorite (NaOCl) (1, 6 and 12%) over 4 time periods (1, 6, 15 and 24 h) to determine if NaOCl denatures B. dendrobatidis DNA sufficiently to prevent its recognition and amplification in PCR tests for the fungus. Soaking in 12% NaOCl denatured 100% of DNA within 1 h. Six percent NaOCl was on average 99.999% effective across all exposure periods, with only very low numbers of zoospores detected following treatment. One percent NaOCl was ineffective across all treatment periods. Under ideal, clean conditions treatment with 6% NaOCl may be sufficient to destroy DNA and prevent cross-contamination of samples; however, we recommend treatment with 12% NaOCl for 1 h to be confident all B. dendrobatidis DNA is destroyed.     

Prevalence of Batrachochytrium dendrobatidis in American bullfrog and southern leopard frog larvae from wetlands on the Savannah River Site, South Carolina

Batrachochytrium dendrobatidis, an aquatic fungus, has been linked to recent amphibian population declines. Few surveys have assessed B. dendrobatidis infections in areas where the disease is suggested to be less virulent and population declines have not been observed, such as southeastern North America. Although adult Rana catesbeiana and Rana sphenocephala from the Savannah River Site, South Carolina collected in 1979 and 1982 were identified as having B. dendrobatidis, it is unknown whether the fungus is currently present at the site or if susceptibility to infection varies among species or wetlands with different histories of environmental contamination. From 15 May through 15 August 2004, we collected R. catesbeiana and R. sphenocephala tadpoles from three wetlands with differing contamination histories on the Savannah River Site, South Carolina. We found B. dendrobatidis in only one of the wetlands we surveyed. Batrachochytrium dendrobatidis infection was identified in 64% of the R. catesbeiana tadpoles sampled and histologically assessed (n=50) from a wetland contaminated with mercury, copper, and zinc. No R. sphenocephala tadpoles from this site (n=50) were infected. In combination with a recently published report, our data suggest that B. dendrobatidis has been present at the Savannah River Site for over 25 yr but has not caused any apparent population declines. This time period is similar to the known presence of 30 yr of B. dendrobatidis in northeastern North America. Our data suggest that R. sphenocephala larvae might be resistant to infection, even when occupying the same wetland as the infected R. catesbeiana. Our survey did not clarify the effects of environmental contamination on infection severity, but our study stresses the importance of additional field surveys to document how this pathogen is affecting amphibians globally.     

Antimicrobial peptide defenses in the salamander, Ambystoma tigrinum, against emerging amphibian pathogens

Skin peptides were collected from living Ambystoma tigrinum larvae and adults and tested against two emerging pathogens, Batrachochytrium dendrobatidis and the Ambystoma tigrinum virus (ATV), as well as bacteria isolated from A. tigrinum. Natural mixtures of skin peptides were found to inhibit growth of B. dendrobatidis, Staphylococcus aureus, and Klebsiella sp., but activity against ATV was unpredictable. Skin peptides collected from salamanders held at three environmentally relevant temperatures differed in activity against B. dendrobatidis. Activity of the A. tigrinum skin peptides was found to be strongly influenced by pH.     

Production of polyclonal antibodies to Batrachochytrium dendrobatidis and their use in an immunoperoxidase test for chytridiomycosis in amphibians

Polyclonal antibodies were produced for diagnosing chytridiomycosis in amphibians. Two sheep and 4 rabbits were inoculated with homogenized whole culture of Batrachochytrium dendrobatidis in Freund's complete adjuvant or triple adjuvant. Antisera from all animals reacted strongly with all stages of B. dendrobatidis and stained the walls, cytoplasm, rhizoids and zoospores in an indirect immunoperoxidase test. Significant cross-reactivity occurred only with some fungi in the Chytridiomycota, and there are no members of this phylum besides B. dendrobatidis that infect frogs. The immunoperoxidase stain is a useful screening test when combined with recognition of the morphology and infection site of B. dendrobatidis.     

Batrachochytrium dendrobatidis: requirement for further isolate collection and archiving

The fungal pathogen Batrachochytrium dendrobatidis (Bd) causes the disease chytridiomycosis, which is lethal to many species of amphibians worldwide. Many studies have investigated the epidemiology of chytridiomycosis in amphibian populations, but few have considered possible host-pathogen coevolution. More specifically, investigations focused on the evolution of Bd, and the link with Bd virulence, are needed. Such studies, which may be important for conservation management of amphibians, depend on access to Bd isolates. Here we provide a summary of known Bd isolates that have been collected and archived in various locations around the world. Of 257 Bd isolates, we found that 53% originate from ranids in the United States. In many cases, detailed information on isolate origin is unavailable, and it is unknown how many isolates are cryo-archived. We suggest the creation of a centralized database of isolate information, and we urge researchers and managers to isolate and archive Bd to facilitate future research on chytridiomycosis.     

Proteomic and phenotypic profiling of the amphibian pathogen Batrachochytrium dendrobatidis shows that genotype is linked to virulence

Population genetics of the amphibian pathogen Batrachochytrium dendrobatidis ( Bd ) show that isolates are highly related and globally homogenous, data that are consistent with the recent epidemic spread of a previously endemic organism. Highly related isolates are predicted to be functionally similar due to low levels of heritable genetic diversity. To test this hypothesis, we took a global panel of Bd isolates and measured (i) the genetic relatedness among isolates, (ii) proteomic profiles of isolates, (iii) the susceptibility of isolates to the antifungal drug caspofungin, (iv) the variation among isolates in growth and phenotypic characteristics, and (v) the virulence of isolates against the European common toad Bufo bufo . Our results show (i) genotypic differentiation among isolates, (ii) proteomic differentiation among isolates, (iii) no significant differences in susceptibility to caspofungin, (iv) differentiation in growth and phenotypic/morphological characters, and (v) differential virulence in B. bufo . Specifically, our data show that Bd isolates can be profiled by their genotypic and proteomic characteristics, as well as by the size of their sporangia. Bd genotypic and phenotypic distance matrices are significantly correlated, showing that less-related isolates are more biologically unique. Mass spectrometry has identified a set of candidate genes associated with inter-isolate variation. Our data show that, despite its rapid global emergence, Bd isolates are not identical and differ in several important characters that are linked to virulence. We argue that future studies need to clarify the mechanism(s) and rate at which Bd is evolving, and the impact that such variation has on the host–pathogen dynamic.     

Retreat sites of rain forest stream frogs are not a reservoir for Batrachochytrium dendrobatidis in northern Queensland, Australia

Chytridiomycosis is a potentially fatal disease of amphibians caused by Batrachochytrium dendrobatidis, and is implicated in declines and extinctions of amphibian populations and species around the world. To cause local host extinction, a disease organism must persist at low host densities. One mechanism that could facilitate this is the ability to persist in the environment. In the laboratory, B. dendrobatidis spreads by both frog-to-frog and environment-to-frog transmission, and can persist on a number of biotic substrates. In the field, B. dendrobatidis has been detected on environmental samples taken during an epidemic, but it is not known if it persists in the environment when endemic. Retreat sites of 2 species of Australian rain forest stream frogs Litoria lesueuri and L. nannotis were sampled 0 to 3 d after occupation during the wet and dry seasons in northern Queensland, Australia, where chytridiomycosis has been endemic for at least 10 yr. The intensity and prevalence of infection in frogs during sampling were comparatively low compared with epidemics. Diagnostic quantitative polymerase chain reaction did not detect B. dendrobatidis in any retreat site samples. It thus appears that retreat sites are not a major environmental source of infection when B. dendrobatidis occurs at low prevalence and intensity on frogs. This suggests that control efforts may not need to eliminate the organism from the environment, at least when prevalence and intensity of infection are low in frogs. Simply treating hosts may be effective at controlling the disease in the wild.     

Surveillance for batrachochytrium dendrobatidis using Mixophyes (Anura: Myobatrachidae) larvae

Fourteen populations of anuran larvae (tadpoles), including three populations of the endangered Fleay's Barred Frog (Mixophyes fleayi) and 11 populations of the common Great Barred Frog (Mixophyes fasciolatus), in creek sites in the southeast region of Queensland were selected. Site selection was based on a history (within the district) of adult frog population declines and/or disappearances or records of infection of adult frogs or larvae by Batrachochytrium dendrobatidis. Larvae were collected once from each creek site between October 2002 and October 2004, and were between Gosner developmental stages 25 and 40. Total body length ranged from 18 mm to 100 mm. Mouthparts were examined under a dissecting microscope for grossly visible abnormalities, and then examined for histologic evidence of B. dendrobatidis. The most consistent mouthpart abnormalities found were multifocal depigmentation of the jaw sheaths and loss or shortening of the tooth rows. At the individual larva level, presence of mouthpart abnormalities was strongly associated with histologic diagnosis of B. dendrobatidis (93%). At least one larva with abnormal mouthparts was detected at 12 of the 14 sites and histologic evidence of B. dendrobatidis was detected at 13 of the 14 sites. These findings suggest that larvae of Mixophyes species are suitable for surveillance for B. dendrobatidis. We conclude that surveillance of B. dendrobatidis where individual larva prevalences of mouthpart abnormalities and histologic evidence of B. dendrobatidis are as high as those observed in this study (66% and 78%, respectively), relatively small numbers of larvae are required to detect these infections. Medium to large larvae (body length >30 mm) were much more likely to be affected than small larvae (body length < or =30 mm), suggesting that larger individuals should be targeted for surveillance.     

Co-localisation of Batrachochytrium dendrobatidis and keratin for enhanced diagnosis of chytridiomycosis in frogs

Chytridiomycosis is a disease of post-metamorphic frogs caused by the fungus Batrachochytrium dendrobatidis and is associated with large declines in frog populations on a global scale. B. dendrobatidis is found only in the keratinised tissues, which include the mouthparts of healthy tadpoles. The epidermis of infected post-metamorphic frogs is thickened (hyperkeratosis) and the superficial layer can sometimes slough. Diagnosis is most commonly performed on stained sections of toe clips or ventral skin. Accurate interpretation can be difficult and requires a high level of expertise, particularly in infected animals exhibiting hyperkeratosis with sloughing. Misdiagnosis can occur when zoosporangia of B. dendrobatidis are shed with the superficial keratin layers. We have developed a staining protocol based on previously described methods to detect both B. dendrobatidis and keratin, to improve the sensitivity and specificity of diagnosis of chytridiomycosis by inexperienced diagnosticians.     

Transmission of Batrachochytrium dendrobatidis within and between amphibian life stages

Chytridiomycosis is an emerging infectious disease caused by the chytrid fungus Batrachochytrium dendrobatidis, which has been implicated in amphibian declines worldwide. The mountain yellow-legged frog Rana muscosa is a declining amphibian species that can be infected by B. dendrobatidis; however, transmission between conspecifics has not been documented. Here, we present experimental evidence that R. muscosa tadpoles can be infected by fungal zoospores and that they can transmit infection to each other and to postmetamorphic animals. We compared several techniques for detecting B. dendrobatidis transmission and found that histology with serial sectioning was able to detect infection before cytology or visual inspections. We also show that R. muscosa tadpoles appear healthy with B. dendrobatidis infection, while postmetamorphic animals experience mortality. In addition, we provide guidelines for visually detecting B. dendrobatidis in R. muscosa tadpoles, which may be useful in other affected species. Field surveys of infected and uninfected populations verify this identification technique.