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Proceedings of the Royal Society B: Biological Sciences logoLink to Proceedings of the Royal Society B: Biological Sciences
. 2018 Dec 12;285(1893):20181894. doi: 10.1098/rspb.2018.1894

Globally invasive genotypes of the amphibian chytrid outcompete an enzootic lineage in coinfections

Thomas S Jenkinson 1,, David Rodriguez 2, Rebecca A Clemons 1, Lucas A Michelotti 1, Kelly R Zamudio 3, L Felipe Toledo 4, Joyce E Longcore 5, Timothy Y James 1,
PMCID: PMC6304064  PMID: 30963903

Abstract

Competition between genotypes is likely to be a key driver of pathogen evolution, particularly following a geographical invasion by distant strains. Theory predicts that competition between disease strains will result in the most virulent strain persisting. Despite its evolutionary implications, the role of strain competition in shaping populations remains untested for most pathogens. We experimentally investigated the in vivo competitive differences between two divergent lineages of the amphibian-killing chytrid fungus (Batrachochytrium dendrobatidis, Bd). These Bd lineages are hypothesized to have diverged in allopatry but been recently brought back into secondary contact by human introduction. Prior studies indicate that a panzootically-distributed, global lineage of Bd was recently introduced into southern Brazil, and is competitively excluding enzootic lineages in the southern Atlantic Forest. To test for differences in competitive ability between invasive and enzootic Brazilian Bd isolates, we coinfected a model host frog system which we developed for this study (Hymenochirus curtipes). We tracked isolate-specific zoospore production over the course of the coinfection experiment with chip-based digital PCR (dPCR). The globally invasive panzootic lineage had a competitive advantage in spore production especially during the first one to four weeks of infection, and on frogs that eventually succumbed to Bd infection. Our study provides new evidence that competitive pressure resulting from the human movement of pathogen strains can rapidly alter the genetics, community dynamics and spatial epidemiology of pathogens in the wild.

Keywords: chytridiomycosis, disease ecology, intraspecific competition

1. Introduction

Competition is a key factor structuring ecological communities [13]. Over time, competition and competitive exclusion contribute to the selection pressure shaping organismal evolution [4]. The competitive exclusion principle predicts that two species (or lineages) should not be able to occupy the same ecological niche indefinitely [5,6]. While this principle is well supported in numerous plant and animal systems, its ecological implications for pathogens remain unclear [7]. Some authors suggest that strain competition will result in pathogen coexistence through host partitioning [8], while others argue that competing strains will be selected for faster growth and higher virulence leading to the exclusion of all but the most virulent lineages [9,10]. Theoretical models support the idea that competing pathogen strains will be under selection for growth rate and virulence, despite an accompanying trade-off in increased host mortality [11,12]. This ‘shortsighted evolution’ scenario predicts the competitive exclusion of all but the most virulent disease strains [13]; however, the prediction remains untested for most diseases (a notable exception being in malaria coinfections) [9]. Here, we examined the outcomes of strain coinfection, and its implications on the disease ecology of a recently emerged fungal pathogen.

Chytridiomycosis is the emerging fungal disease implicated in population declines and extinctions of amphibians worldwide [1416]. Caused by the chytridiomycete fungus Batrachochytrium dendrobatidis (Bd) [17], this disease has emerged as one of the most significant contemporary threats to global amphibian biodiversity [18]. In many regions of the globe Bd is newly arrived and actively spreading [1921]. In other regions Bd appears to be enzootic and in stable equilibrium with its associated hosts [22]. This is the case in the Atlantic Forest of southeastern Brazil where two deeply divergent lineages of Bd co-occur in a number of contact zones [23,24]. In the Atlantic Forest region, the globally distributed, panzootic clone of Bd (termed Bd-GPL—Global Panzootic Lineage) [25] and a regional enzootic lineage (Bd-Brazil, also known as Bd-Asia-2/Brazil) [23,26] occupy overlapping ranges.

In addition to Bd-GPL and Bd-Brazil, two additional lineages of Bd have now been recognized from southern Africa (Bd-Cape) and east Asia (Bd-Asia-1; which includes Bd-CH) [2527]. We now know that differences in virulence exist among these lineages [25,26,28,29]. We also know that multi-lineage coinfections by diverse Bd genotypes occur in natural populations (e.g. the Bd-GPL isolate CLFT024/0 and hybrid isolate CLFT024/2 were both collected from the same Hylodes cardosoi tadpole host) [23,30]. Coinfections in nature provide opportunities for competition which can occur directly or indirectly. In the case of direct competition, individuals directly exclude one another from a limited resource. Alternatively, competition may be indirect, where competitive interactions are mediated through the antagonistic response of a resource species, or host immune response in the case of pathogens. Indirect competition is well documented in fungi [31,32], and in pathogen species in general [33]; and both modes of competition can result in the exclusion of a weaker competitor [34,35]. The possibilities for diverse Bd coinfections to occur are growing continually as disease lineages are increasingly transported away from their native ranges by anthropogenic activity [26,36]. Despite the potential for competitive dynamics to shape disease genotypes present in a pathogen population over time, little work to date has explored the nature of competition between any of the divergent Bd lineages or considered the population-level outcomes of genotype competition.

Our study was motivated in-part by the striking geographical distribution of enzootic Bd-Brazil we observed in the field. Despite ample surrounding habitat predicted to be highly suitable for Bd growth in the southern Atlantic Forest [37], Bd-Brazil is found only from a small handful of sampling sites. The population structure of the two Bd lineages in the Brazilian Atlantic Forest suggests that Bd-GPL has been rapidly expanding [24], and excluding Bd-Brazil from its former range. To evaluate whether competitive differences are shaping the genetic structure of this expanding pathogen population, we conducted a coinfection experiment using a novel amphibian host model. The specific goals of this study were to quantify the relative performance of Bd-GPL and Bd-Brazil strains when inoculated onto the same host resource, and to develop a model Bd host system suitable for standardizing future laboratory-based virulence and transmission studies. Our results support strain competition as an ecological force capable of shifting pathogen genotype frequencies in mixed populations and have wide-ranging implications for understanding the evolution of pathogenicity traits following human-mediated pathogen introductions.

2. Material and methods

(a). Experimental design

To investigate if fitness differences exist among Bd strains, we tracked the temporal population genetics of Bd-GPL × Bd-Brazil coinfections in experimental amphibian populations. We measured differences in zoospore production at four time points over the course of a 10-week experiment, and used chip-based digital PCR (dPCR) to quantify a mitochondrial SNP (Bdmt26360) that distinguishes Bd-GPL from Bd-Brazil in a mixed sample.

We used the aquatic, western dwarf clawed frog (Hymenochirus curtipes, Pipidae) as the host for this study. Hymenochirus curtipes is tolerant to Bd infection at low levels but may succumb to disease at high pathogen loads [38,39]. Hymenochirus curtipes is also available from commercial suppliers in the aquarium trade, allowing for the iteration of this study by separate research groups. This species is completely aquatic and is amenable to housing in groups [40], which allowed our study to simulate the dynamics of active strain transmission within a host population. Finally, H. curtipes is native to the Congo basin of central Africa. Having been recently collected from Brazil, these Bd isolates will not have encountered the H. curtipes host environment in their recent ecological histories. This common garden design provides a competitive landscape distinct from the host diversity available to either strain within their current ranges in the Atlantic Forest.

We selected two Bd-GPL isolates and two Bd-Brazil isolates to coinfect in the four possible combinations between the represented lineages (figure 1a). This design addressed competitive differences between Bd-GPL and Bd-Brazil while accounting for possible isolate-to-isolate differences within each lineage. The study isolates were all recently collected from the lineage contact zones in the Brazilian Atlantic (figure 1b). We passaged the experimental isolates minimally in culture (table 1) to prevent major genetic or phenotypic changes under laboratory conditions [41,42]. Our experimental units consisted of 20 aquarium tanks (35 l of water) housing small populations (n = 5) of western dwarf clawed frogs. Each experimental population was randomly assigned to one of the four infection treatments, and each treatment was replicated in five experimental tanks (n = 100 animals total) (electronic supplementary material, table S1). Full details of our animal care procedures and Bd culture methods are available in the electronic supplementary material.

Figure 1.

Figure 1.

Experimental design of the pairwise strain competition experiment. (a) Two Bd-GPL and two Bd-Brazil strains were coinfected in all four possible GPL × Brazil treatment combinations. We repeated each treatment five times for a total of 20 tanks. (b) Collection localities, dates and isolate codes for the strains examined in this study.

Table 1.

Bd isolates used for this experiment.

designation isolate year passages host locality
GPL-A CLFT073 2013 9 Aplastodiscus sp. Serra dos Órgãos National Park, Rio de Janeiro
Brazil-A CLFT070 2013 9 Hylodes japi Serra do Japi, Jundiai, São Paulo
GPL-B CLFT137 2014 6 Hylodes cardosoi Serra da Graciosa, Morretes, Paraná
Brazil-B CLFT150 2014 6 Hylodes cardosoi Serra da Graciosa, Morretes, Paraná

For the coinfections, our goal was not to induce or measure mortality as an effect, but rather to inoculate hosts with a dose of Bd that would result in the maintenance of infection over the study period. Each host population (n = 5) was exposed to a 20 ml zoospore bath containing 107 infective zoospores from each of two competing isolates (combined inoculum concentration = 106 zoospores ml−1; total exposure with both isolates = 2 × 107 zoospores). The exposure baths were incubated at 19°C to 20°C for 6 h. After the exposures, all animals were released back to their respective tanks along with the inoculation bath and monitored daily for mortality or signs of morbidity.

(b). Data collection

We monitored infection progress for 70 days (10 weeks) after inoculation by swabbing the animals weekly with sterile skin swabs (MW 113, Medical Wire and Equipment Co.). We swabbed the interdigital webbing of each limb five times and both lateral surfaces of the abdomen five times (30 passes total). We employed the same procedure to swab any dead or moribund individuals (n = 38) encountered during daily health checks. We extracted genomic DNA from skin swabs with 50 µl of PrepMan Ultra sample preparation reagent (Thermo Fisher Inc.). For routine monitoring of Bd infection through the course of the experiment, we performed qPCR assays on the weekly skin swabs [43]. Reaction conditions and cycling parameters are presented in electronic supplementary material, table S2.

To assess the outcome of coinfection, we chose four equally spaced, temporal samples (weeks 1, 4, 7, and 10) for isolate identification and quantification with the chip-based, QuantStudio 3D digital PCR system (Thermo Fisher Inc.) following the manufacturer's protocols. Chip-based dPCR is ideal for detecting rare allelic variation in mixed samples [44,45]. The dPCR system partitions a duplexed, lineage-specific TaqMan assay into a PCR reaction chip composed of 20 000 nanowells. We used qPCR-estimated quantification of total DNA to adjust each sample dilution so that some wells received target DNA, while others did not. Any well that received a target sequence which was successfully amplified in the PCR step released a specific fluorescent signal. Probe sequences, dPCR reaction conditions and cycling parameters are presented in electronic supplementary material, table S3. Post-dPCR, we used the QuantStudio 3D digital PCR chip reader to detect the fluorescence signal of reporter dyes from each nanowell (from either the VIC-tagged Bd-GPL probe or the FAM-tagged Bd-Brazil probe), and used the dPCR measured zoospore density (GE µl−1) of each isolate as our indicator of competitive ability.

At week 7 we euthanized a sample of five individuals from the coinfection experiment to isolate Bd cultures. We microscopically scanned interdigital tissue for evidence of infection, and isolated cultures following Longcore et al. [46]. These re-isolations provided one additional way to assess the genotypic winners of competitive coinfections. We obtained five isolates and determined their genotypes using two multilocus sequence type markers known to differentiate the major Bd lineages (see electronic supplementary material, Supplementary methods).

(c). Data analyses

Even closely related isolates of Bd can vary significantly in molecular marker copy number [47,48]. We addressed this by first determining the degree of copy number variation among isolates for the mitochondrial assay marker. We made isolate-specific 106 zoospore standards for each of the experimental isolates by counting zoospores with a haemocytometer as before. We performed the same dPCR assays on a serial dilution of each isolate-specific standard (103, 104, 105 and 106). We constructed standard curves, and calculated the slope of the linear relationship between marker concentrations (copies µl−1). For each isolate, we multiplied the slope of its dPCR standard curve by observed copy concentrations to determine zoospore density (GE µl−1). To improve the variance homogeneity in zoospore density across partitions (by lineage, by isolate, by time point), we log transformed (log10 (x + 1)) observed zoospore densities before the analyses. Because of the non-normal distributions of these data, we used non-parametric methods for statistical hypothesis testing, which were performed in R v. 3.4.2 [49].

3. Results

(a). Bd infection over 10 weeks

From week 1 to week 6 post-inoculation, mean infection loads in all tanks (assessed by qPCR) plateaued at 996–5770 GE per swab. After the sixth week, infection loads dropped rapidly, continuing to the end of the experiment (mean: 891–50 GE per swab; electronic supplementary material, figure S3). Infection loads dropped by an overall rate of 311.5 GE per week (linear regression: slope = −311.5, r2 = 0.557, p = 0.008). Many of the H. curtipes hosts suppressed (or fully recovered from) Bd infection over the 10-week period; however, individual host outcomes ranged widely. Of the 100 starting animals, 21% of individuals tested negative for Bd infection by the end of 10 weeks, while 38% of individuals died or were euthanized because of disease signs. The time to death of succumbing individuals was not associated with any of the four treatments (Kruskal–Wallis rank-sum test χ2 = 0.63, d.f. = 3, p = 0.889).

(b). Competitive effects between Bd-GPL and Bd-Brazil

We partitioned the weekly zoospore densities by lineage to test for differences in spore production. Bd-GPL produced higher spore densities than Bd-Brazil at all time points (figure 2). We observed differences in zoospore density between lineages as a function of time (Kruskal–Wallis rank-sum test χ2 = 213.84, d.f. = 7, p < 0.001). We assessed pairwise differences between these lineage partitions post hoc using Dunn's test of multiple comparisons with a Bonferroni correction. Our Dunn's test comparisons showed that Bd-GPL produced more spores than Bd-Brazil early in the infection, during week 1 (corrected p < 0.001) and week 4 (corrected p < 0.001). By week 7, Bd-GPL spore densities were reduced from previous weeks, whereas mean Bd-Brazil spore density increased from the previous time point. Bd-GPL still produced more spores on average than Bd-Brazil, but the differences in density were statistically indistinguishable (corrected p = 0.080). Finally, by week 10, spore densities continued to drop for both strains. Again, by week 10 mean Bd-GPL spore densities were greater than those of Bd-Brazil, but not significantly so (corrected p = 0.370). Based on DNA sequences of two population-informative markers, the five cultures we isolated at seven weeks post-inoculation were all Bd-GPL.

Figure 2.

Figure 2.

Zoospore production by Bd-GPL is more robust than Bd-Brazil. Bd-GPL produces significantly more spores in the early stages of the 10-week coinfection experiment. Box plots show the median and interquartile zoospore densities (log (GE µl−1 + 1)) for Bd-GPL (red) and Bd-Brazil (blue) at four sampled time points. Whiskers show the range for all observations.

(c). Differences in competitive fitness among isolates

We partitioned spore density data to test for fitness differences between our four individual Bd isolates. Within each lineage, we observed significantly superior and inferior competitor isolates (figure 3). Both GPL-B and Brazil-B were significantly better spore producers than their co-lineage counterparts GPL-A and Brazil-A (Kruskal–Wallis rank-sum test χ2 = 283.2, d.f. = 15, p < 0.001). We again assessed differences post hoc between isolate partitions using Dunn's test. In week 1, both Bd-GPL isolates and the competitively superior Brazil-B isolate produced higher zoospore densities than the inferior Brazil-A. In week 4, the competitively inferior GPL-A produced a lower density of spores than GPL-B, but this difference was not significant (corrected p > 0.999).

Figure 3.

Figure 3.

Zoospore production over 10 weeks varies significantly by isolate strain. Box plots show the median and interquartile zoospore densities (log (GE µl−1 + 1)) at sampled time points for the two Bd-GPL (red) and the two Bd-Brazil (blue) isolates studied. Whiskers show the range for all observations.

The average increase in Bd-Brazil spore density at week 7 was driven entirely by the competitively superior Brazil-B isolate. It was at week 7 that the competitive differences among isolates were most pronounced. For both lineages, the competitively superior isolates (GPL-B and Brazil-B) produced higher zoospore densities than their competitively inferior counterparts in the same lineage (GPL-A and Brazil-A). However, the competitively superior GPL-B isolate still produced higher average spore densities than the competitively superior Brazil-B (although not significantly; corrected p > 0.999). By week 10, the most competitive of the four isolates (GPL-B) produced higher median spore densities than the other isolates; however, this trend was only significant compared to the least competitive of the isolates (Brazil-A; corrected p = 0.011).

(d). Competitive outcomes differed by treatment tank

To visualize the magnitude of competitive differences at the level of individual tanks, we plotted the difference between Bd-GPL and Bd-Brazil spore densities (Δ = (Bd-GPL GE µl−1) − (Bd-Brazil GE µl−1)) taken from each host animal (figure 4). A positive delta indicated a greater density of Bd-GPL spores, while negative deltas indicated greater densities of Bd-Brazil spores. Overall, mean deltas through the experiment were positive (mean week 1 Δ = 69.98 GE µl−1, mean week 4 Δ = 93.65 GE µl−1, mean week 7 Δ = 7.87 GE µl−1, mean week 10 Δ = 11.84 GE µl−1).

Figure 4.

Figure 4.

Differences in zoospore densities by individuals and tanks. Bar plots represent the difference (Δ) between Bd-GPL and Bd-Brazil zoospore densities [Δ = (log (Bd-GPL (GE µl−1) + 1) − log (Bd-Brazil (GE µl−1) + 1))] for each host. Bars with positive values (red) show individuals in which Bd-GPL spore densities are greater than Bd-Brazil. Bars with negative values (blue) show the degree of Bd-Brazil advantage. Missing bars indicate individuals that have either died or cleared the disease over the course of this experiment.

We observed that competitive differences were greatest in the first part of the infection experiment (week 1 and 4) and grew weaker as the infection was cleared (week 7 and 10). The variation in competitive outcomes was largely shared across individuals in a tank. For example, all living individuals in Tank R during week 4 had strong negative Δs, showing that Brazil-B was the dominant isolate across host individuals at that time point. In the less common case where the Bd-Brazil strain had the advantage at the end of the experiment (figure 4; tanks Q and R, week 10), treatments were inoculated with a GPL-B × Brazil-B pairing (electronic supplementary material, table S1). This pairing, however, did not always yield a Bd-Brazil advantage (figure 4; tanks S and T, week 10). Brazil-B was also outperformed by GPL-A in all replicates (figure 4; tanks K through O), underscoring the complex nature of strain hierarchy.

(e). Zoospore densities at host death

The zoospore densities from post-mortem skin swabs ranged an order of magnitude greater than those from live animals (spore densities from surviving animals: approximately 0.0–103 GE µl−1; post death: approximately 0.0–2.0 × 104 GE µl−1). Because of this discrepancy in range, we analysed zoospore densities from the post-mortem swabs separately from the data presented above. Bd-GPL zoospore densities were higher than Bd-Brazil spore densities on dead individuals (Wilcoxon rank-sum test W = 1309, p < 0.001; figure 5). As with spore densities on live individuals, we observed differences in average spore density between the more and less competitive isolates, but the differences were not significant at α = 0.05. A linear regression showed a slight decrease (slope = −0.184) in post-mortem Bd-GPL zoospore densities over the course of 10 weeks (r2 = 0.140, p = 0.016) and no temporal trend in post-mortem Bd-Brazil spore densities (r2 = 0.001, p = 0.854).

Figure 5.

Figure 5.

Zoospore densities in post-mortem skin swabs. (a) Spore densities (log (GE µl−1 + 1)) over time. Bd-GPL spore density is shown in red diamonds, and Bd-Brazil spore density is shown in blue circles. (b) Difference in all Bd-GPL and Bd-Brazil zoospore densities at death. Box plots show the median and interquartile zoospore densities (log (GE µl−1 + 1)) for Bd-GPL (red) and Bd-Brazil (blue). Whiskers show the range for all observations.

4. Discussion

Our results demonstrate that Bd genotypes differ in reproductive ability when coinfecting the same hosts. We found differences in competitive fitness between major lineages of Bd (Bd-GPL and Bd-Brazil) and a hierarchical relationship of competitive ability within the lineages. We suggest that strain to strain competition can result in the eventual replacement of existing pathogen diversity resulting in populations of the most reproductively competitive genotypes. Given that the international amphibian trade is closely associated with the long-distance transport of major Bd lineages [23,25,26], we predict a future escalation of pathogen transmissibility though the competitive dynamics we describe here. The implications of our results grow in urgency as diverse Bd strains are increasingly transported between continents, which expands opportunities for secondary contact between divergent genotypes. The rapid genetic turnover of pathogen populations though competition holds the potential to alter disease outcomes at regional scales—potentially presenting a conservation risk where an earlier, enzootic strain did not [50].

Our study showed significant differences in relative fitness between Bd-GPL and Bd-Brazil at the critical phase of infection for successful transmission—the peak of zoospore production and host mortality in the first one to four weeks after inoculation [51,52]. It is clear that the ecological and evolutionary consequences of strain competition depend crucially on whether competitive dynamics affect transmission to new hosts [53]. Our measure of competitive success in this study—zoospore production—is directly tied to the mode of transmission for Bd, making the competitive advantage we observed in the laboratory likely to translate to increased transmission success in the field.

Under coinfection, each Bd strain is also in conflict with the host's immune system. Most (62%) of our H. curtipes hosts in this experiment either suppressed or completely cleared Bd infections after 10 weeks. In an open, natural system with an available pool of new, susceptible individuals, we expect that the probability of propagating infection through a host community will favour strains with the ability to persist and produce greater spore densities than their conspecific competitors. Based on our data, we predict that a Bd-GPL epizootic is more likely to spread in a susceptible population owing to differences in propagule output over the infection cycle. Because the host immunological landscape in our experiment is ecologically novel to the isolates collected in southeastern Brazil, the patterns of competitive survivorship we observed may be relevant to inferring outcomes of Bd strain coinfection generally as Bd lineages invade news habitats—a scenario repeated in diverse habitats worldwide through anthropogenic pathogen transport [26].

The precise connection between increased spore production and its implications for virulence evolution in Bd remains an open area of research. Prior studies have shown that Bd phenotypes with greater rates of spore production cause increased host mortality [41]. This suggested a simple relationship between virulence (host tissue damage) and the production of reproductive propagules. Though not the main focus of our coinfection study, our pilot experiments on single isolate virulence preliminarily suggest that the most reproductively successful Bd-GPL isolates were not necessarily the most lethal. Zoospore production in our single isolate infections did not directly relate to host mortality (electronic supplementary material, figure S2, host survival versus spore production), nor did host mortality in single isolate inoculations coincide with reproductive success under coinfection (figure 3 versus electronic supplementary material, figure S2). While this pilot study should be repeated with a larger sample size, the initial results suggest that Bd isolates may vary in traits that interact in yet unknown ways with the host immune system. Our results point to the evolutionary links between isolate virulence and spore transmission as an intriguing area of future investigation in Bd.

At present, the evolutionary ecology of genetically diverse pathogen populations remains poorly understood. This is especially true for eukaryotic pathogens such as fungi [54]. For many bacterial and viral pathogens, a theoretical constraint on virulence is imposed by the inherent trade-offs between host exploitation and transmission [7]. Does this constraint hold true for emerging mycoses with broad host ranges such as Bd? Our understanding of the link between transmission and virulence in fungal pathogens—and in eukaryotic pathogens more broadly—still must be inferred from the few eukaryotic systems studied thus far.

Among the few well-studied examples in the eukaryotes, Plasmodium chabaudi (Apicomplexa; causing rodent malaria) is constrained by the reproduction/transmission trade-off [55]. In this example, the dominance of a specific clone in a mixed infection did not translate to increased transmission success of that clone to new hosts. Like this example, our results showed that the better spore producer was not the deadliest. These observations provide support for the hypothesis that extreme Bd virulence may come at a cost to transmissibility. Ultimately, the primary trait allowing Bd-GPL to rise to global prominence may in fact be its transmissibility through reproductive characteristics rather than virulence. In previous studies [28], the virulence of Bd-GPL isolates were not always greater than those of Bd-Brazil as measured by host survival. Therefore, strain competition between divergent lineages may be one situation where the virulence/transmission trade-off becomes more critical to determining disease outcomes.

In addition to the differences in zoospore production we observed between Bd lineages, we also found that zoospore production by specific isolates varied within each lineage. These results agree with previous studies showing phenotypic variation among closely related genetic isolates of Bd [28,56,57]. Although genomic changes and virulence attenuation can occur in Bd isolates serially passaged over long periods of time [41,42,58], we do not believe that laboratory passage was a contributing factor in the results we observed. Prior studies documenting in vitro changes were based on cultures passaged over 30 times in the span of 6 years. When our inoculations took place, all experimental isolates had been passaged either six or nine times. We also controlled for passage history by selecting paired Bd-GPL and Bd-Brazil isolates collected contemporaneously and passaged an equal number of times in culture. Our results showed that the Bd-GPL isolate with nine passages significantly outperformed its Bd-Brazil counterpart with nine passages. The same pattern held for the Bd-GPL and Bd-Brazil pair with six passages.

Along with the ecological and evolutionary implications of these results, our study serves as a proof of concept for two new tools to improve our understanding of amphibian chytrid ecology and evolution. First, dPCR is a viable tool for the detection of rare genotypes in mixed pathogen populations. The ability to simultaneously quantify and genotype samples with high accuracy makes this tool extensible to a range of studies of mixed infections within a pathogen population. For example, the dPCR probes could be readily adapted to distinguish between Bd and its congeneric sister taxon Batrachochytrium salamandrivorans [59]. The ability to detect one variant copy in 1–5 µl of sample outperforms traditional duplexed qPCR, which is prone to allele drop out at these template concentrations [60]. We also describe a potential model host in which to test Bd phenotype across a standardized host species, Hymenochirus curtipes. At present, virulence studies are typically conducted on haphazard assemblages of locally available species [61], which makes the replication and comparison of experiments across research groups difficult. Hymenochirus curtipes has a number of traits that make it a practical model host to explore virulence phenotype across Bd lineages. It is susceptible to chytridiomycosis, unlike Xenopus laevis, and its fully aquatic nature and small body size simplifies husbandry while allowing for facile disease transmission. Hymenochirus curtipes is also commercially available and easy to breed [40]. Finally, the ability to expose animals to a prolonged 30°C incubation period in order to clear incoming chytridiomycosis is a major advantage not present in many amphibian species.

The experimental system we describe here provides a base upon which to test more complex questions about the ecology of pathogen communities. For example, our current study only explored the outcomes of simultaneous coinfection. Priority effects are known to play a large role in ecological structuring [62], especially within the fungi [63,64]. An immediate next area of research is to explore the effects of sequentially inoculated strains and address the roles of priority and contingency on the competitive structuring of microbial populations. Another potential elaboration on this system could be introducing new susceptible hosts at various time points in the experiment to better understand transmission dynamics over longer experimental time scales. Together, these types of studies will allow a better understanding of how pathogen populations assemble, and provide empirical parameters to tailor disease dynamic predictions to emerging fungal pathogens.

Supplementary Material

Electronic Supplementary Material for Jenkinson et al
rspb20181894supp1.pdf (310.1KB, pdf)

Acknowledgements

We would like to acknowledge Joice Ruggeri, Anat M. Belasen and the veterinary team from the University of Michigan Laboratory Animal Medicine Unit for support and advice on animal care. We also thank two anonymous reviewers for their helpful suggestions on improving this manuscript.

Ethics

We performed all investigations involving live vertebrate animals following protocols approved by the University of Michigan Institutional Animal Care and Use Committee (IACUC protocols PRO00005605 and PRO00007691).

Data accessibility

The datasets analysed for this article are available from the Dryad Digital Repository at http://dx.doi.org/10.5061/dryad.1qh6772 [65].

Authors' contributions

T.S.J., D.R., L.F.T., K.R.Z., and T.Y.J. conceived of and designed the study. T.S.J., D.R., R.A.C., L.A.M., J.E.L., and T.Y.J. performed laboratory work. T.S.J., D.R., and T.Y.J. analysed the data. T.S.J. and T.Y.J. wrote the article. All authors gave their final approval for publication.

Competing interests

We declare we have no competing interests.

Funding

This study was supported by a Doctoral Dissertation Improvement Grant from the United States National Science Foundation (DEB-1601259), the São Paulo State Research Foundation (FAPESP no.2014/25358-3), the Brazilian National Council for Scientific and Technological Development (CNPq no.405285/2013-2, no.302589/2013-9, no.300896/2016-6), and the Research Enhancement Program at Texas State University (no.9000001537).

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Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Data Citations

  1. Jenkinson TS, Rodriguez D, Clemons RA, Michelotti LA, Zamudio KR, Toledo LF, Longcore JE, James TY. 2018. Data from: Globally invasive genotypes of the amphibian chytrid outcompete an enzootic lineage in coinfections Dryad Digital Repository. ( 10.5061/dryad.1qh6772) [DOI] [PMC free article] [PubMed]

Supplementary Materials

Electronic Supplementary Material for Jenkinson et al
rspb20181894supp1.pdf (310.1KB, pdf)

Data Availability Statement

The datasets analysed for this article are available from the Dryad Digital Repository at http://dx.doi.org/10.5061/dryad.1qh6772 [65].


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