Effect of Temperature on Host Response to Batrachochytrium dendrobatidis Infection in the Mountain Yellow-legged Frog (Rana muscosa)

Similar documents
EMERGING INFECTIOUS DISEASE AS A PROXIMATE CAUSE OF AMPHIBIAN MASS MORTALITY

Transmission of Batrachochytrium dendrobatidis within and between amphibian life stages

INVESTIGATING THE POPULATION-LEVEL EFFECTS OF CHYTRIDIOMYCOSIS: AN EMERGING INFECTIOUS DISEASE OF AMPHIBIANS

Distribution Limits of Batrachochytrium dendrobatidis: A Case Study in the Rocky Mountains, USA

INTRODUCTION. Blacksburg, Virginia 24061, USA 4 Corresponding author: (

Use of Immunohistochemistry to Diagnose Chytridiomycosis in Dyeing Poison Dart Frogs (Dendrobates tinctorius)

Nowhere to hide: impact of a temperature-sensitive amphibian pathogen along an elevation gradient in the temperate zone

Introduction. Abstract

Annual assessment of Chytrid fungus prevalence amongst endangered native Fijian ground frog populations on Viwa Fiji Islands Project ID:

Evan H Campbell Grant Northeast Amphibian Research and Monitoring Initiative US Geological Survey Patuxent Wildlife Research Center

Host species determines whether infection load increases beyond disease-causing thresholds following exposure to the amphibian chytrid fungus

Amphibian chytridiomycosis: strategies for captive management and conservation

[Byline: Erica Bree Rosenblum1*, Jamie Voyles2, Thomas J. Poorten1, Jason E. Stajich3,4

Spread of Chytridiomycosis Has Caused the Rapid Global Decline and Extinction of Frogs

Chapter 4. Probability Theory. 4.1 Probability theory Events

Species-level correlates of susceptibility to the pathogenic amphibian fungus Batrachochytrium dendrobatidis in the United States

The ecology and impact of chytridiomycosis: an emerging disease of amphibians

Survival of three species of anuran metamorphs exposed to UV-B radiation and the pathogenic fungus Batrachochytrium dendrobatidis

CHYTRIDIOMYCOSIS caused by the fungal pathogen

Batrachochytrium dendrobatidis not found in rainforest frogs along an altitudinal gradient of Papua New Guinea

Interspecific Variation in Susceptibility of Frog Tadpoles to the Pathogenic Fungus Batrachochytrium dendrobatidis

Principal Investigator: Roland Knapp; Co-principal Investigator: Vance Vredenburg

PATHOGENICITY OF BATRACHOCHYTRIUM DENDROBATIDIS IN LARVAL AMBYSTOMATID SALAMANDERS

Herpetological Review

Biological Conservation

Resistance, tolerance and environmental transmission dynamics determine host extinction risk in a load-dependent amphibian disease

AMPHIBIAN AND REPTILE DISEASES

Chytridiomycosis: a global threat to amphibians

4/18/2013 FUNGUS MAP WHAT IS SAPROLEGNIASIS

Low Prevalence of Chytrid Fungus (Batrachochytrium dendrobatidis) in Amphibians of U.S. Headwater Streams

Effects of the Amphibian Chytrid Fungus and Four Insecticides on Pacific Treefrogs (Pseudacris regilla)

The ecology of chytridiomycosis in red-legged frog (Rana aurora) tadpoles. Phineas Hamilton B.Sc., University of Victoria, 2006

Endemicity of chytridiomycosis features pathogen overdispersion

Methodologies for the Care, Maintenance, and Breeding of Tropical Poison Frogs

Distribution and environmental limitations of an amphibian pathogen in the Rocky Mountains, USA

Higher temperature variability increases the impact of Batrachochytrium dendrobatidis and shifts interspecific interactions in tadpole mesocosms

SUSCEPTIBILITY TO THE AMPHIBIAN CHYTRID FUNGUS VARIES WITH ONTOGENY IN THE DIRECT-DEVELOPING FROG ELEUTHERODACTYLUS COQUI

Impact of a Chytrid-related mortality event on a population of the Green and Golden Bell Frog Litoria aurea

Altitudinal distribution of chytrid (Batrachochytrium dendrobatidis) infection in subtropical Australian frogs

Amphibian Population Declines and deformities are useful phenomena to illustrate concepts in evolutionary biology

Integrative and objective science is the best link between amphibian decline research and conservation on the ground

Batrachochytrium dendrobatidis: Chytrid disease

Tasmanian Frog and Chytrid monitoring 2014: Executive summary

MICROORGANISMS AND AMPHIBIANS

Host species composition influences infection severity among amphibians in the absence of spillover transmission

AMPHIBIAN CHYTRID FUNGUS (BATRACHOCHYTRIUM

EFFECTS OF CANOPY COVER ON THE LANDSCAPE EPIDEMIOLOGY OF AN AMPHIBIAN CHYTRID FUNGUS STACY ELIZABETH BEYER THESIS

Skin sloughing rate increases with chytrid fungus infection load in a susceptible amphibian

Ecotoxicology of Declining Amphibian Populations

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

Linking manipulative experiments to field data to test the dilution effect

Effects of an Infectious Fungus, Batrachochytrium dendrobatidis, on Amphibian Predator-Prey Interactions

What Drives Chytrid Infections in Newt Populations? Associations with Substrate, Temperature, and Shade

THREAT ABATEMENT PLAN

Evolution and pathogenicity in the deadly chytrid pathogen of amphibians. Erica Bree Rosenblum UC Berkeley

Goal of the Lecture. Lecture Structure. Tadpole Development, Ecology, and Metamorphosis

3/24/10. Amphibian community ecology. Lecture goal. Lecture concepts to know

v o l u m e 1 5 n u m b e r Disease Ecology and Wildlife Health in the Greater Yellowstone Ecosystem

HIGH PREVALENCE AND SEASONAL PERSISTENCE OF AMPHIBIAN CHYTRID FUNGUS INFECTIONS IN THE DESERT-DWELLING AMARGOSA TOAD, ANAXYRUS NELSONI

Spatial dynamics and population impacts of disease in threatened amphibians

Purpose. Potential causes for amphibian declines in Puerto Rico. Three species presumably extinct! Long Term Data of Transect Surveys :

Title: Predation by zooplankton on Batrachochytrium dendrobatidis: Biological control of the

Predation by zooplankton on Batrachochytrium dendrobatidis: biological control of the deadly amphibian chytrid fungus?

A SURVEY FOR THE PRESENCE OF THE AMPHIBIAN CHYTRID FUNGUS (BATRACHOCHYTRIUM DENDROBATIDIS) IN TASMANIA

Applying Critical Thinking to the Amphibian Decline Problem

Methodologies for the Care, Maintenance, and Breeding of Tropical Poison Frogs Scott P. McRobert Published online: 04 Jun 2010.

Skin microbiome composition and diversity across Anaxyrus boreas developmental stages

Mechanisms behind the successful invasion of American Bullfrogs (Rana catesbeiana) in the Northwest United States

Chytridiomycosis and Seasonal Mortality of Tropical Stream-Associated Frogs 15 Years after Introduction of Batrachochytrium dendrobatidis

Sciences Graduate Program, Oregon State University, 104 Wilkinson Hall, Corvallis, OR 97330, USA; and

Distribution of Batrachochytrium dendrobatidis and pathology in the skin of green tree frogs Litoria caerulea with severe chytridiomycosis

CURRICULUM VITAE Jesse L. Brunner

Antifungal efficacy of F10SC veterinary disinfectant against Batrachochytrium dendrobatidis

Curriculum Vitae John Matthew Romansic 1203 E. Curtis St. Tampa, FL (813)

TRANSLOCATION AND CONSERVATION OF HELLBENDERS. A Thesis. Presented to. the Faculty of the Graduate School. at the University of Missouri

The impact of the Amphibian Chytrid Fungus Batrachochytrium dendrobatidis on a Green and Golden Bell Frog Litoria aurea

Welcome to General Ecology PCB 4043

Final Report Prepared by: Jonathan E. Kolby

Amphibian species traits, evolutionary history, and environment predict. Batrachochytrium dendrobatidis infection patterns, but not extinction risk

at some point of their lives (Just et al., 1981). Such a change normally involves the

LETTERS TO THE EDITOR

An Epidemiological Approach to the Dynamics of Chytridiomycosis on a Harlequin Frog Population

From The Cover: Emerging infectious disease and the loss of biodiversity in a Neotropical amphibian community

Curriculum Vitae John Matthew Romansic 1203 E. Curtis St. Tampa, FL (813)

Saprolegnia: Amphibian Killer? Discussion Outline. What is Saprolegnia? 4/6/2009. What is Saprolegnia? What does Saprolegnia do to amphibians?

CHAPTER. Population Ecology

Ranavirus could facilitate local extinction of rare amphibian species

Supporting Information

The Prevalence of Chytridiomycosis in the Southern Appalachians

Differences in sensitivity to the fungal pathogen Batrachochytrium dendrobatidis among amphibian populations

Pathogen invasion and non-epizootic. the last century

Occurrence and Prevalence of Chytrid Fungus (Batrachochytrium dendrobatidis) in Amphibian Species of Alberta

AN INVESTIGATION INTO THE OCCURRENCE OF BATRACHOCHYTRIUM DENDROBATIDIS INFECTION IN PLETHODONTID SALAMANDER COMMUNITIES OF ROBINSON FOREST

ENVIRONMENTAL DNA (EDNA) SAMPLING FOR AMPHIBIAN PATHOGENS

Individual and combined effects of multiple pathogens on Pacific treefrogs

THE ECOLOGY OF CHYTRIDIOMYCOSIS, AN EMERGING INFECTIOUS DISEASE OF AUSTRALIAN RAINFOREST FROGS

The Effects of Temperature Frequency and Magnitude on Lithobates sylvaticus and Hyla versicolor

Thursday. Threshold and Sensitivity Analysis

Do emerging infectious diseases have a role in the decline and extinction of species? 1. Global loss of biodiversity 2. Emerging infectious diseases

Phenotypic variation 3/6/17. Phenotypic plasticity in amphibians

Transcription:

Effect of Temperature on Host Response to Batrachochytrium dendrobatidis Infection in the Mountain Yellow-legged Frog (Rana muscosa) Authors: Sara E. Andre, John Parker, and Cheryl J. Briggs Source: Journal of Wildlife Diseases, 44(3) : 716-720 Published By: Wildlife Disease Association URL: https://doi.org/10.7589/0090-3558-44.3.716 BioOne Complete (complete.bioone.org) is a full-text database of 200 subscribed and open-access titles in the biological, ecological, and environmental sciences published by nonprofit societies, associations, museums, institutions, and presses. Your use of this PDF, the BioOne Complete website, and all posted and associated content indicates your acceptance of BioOne s Terms of Use, available at www.bioone.org/terms-of-use. Usage of BioOne Complete content is strictly limited to personal, educational, and non-commercial use. Commercial inquiries or rights and permissions requests should be directed to the individual publisher as copyright holder. BioOne sees sustainable scholarly publishing as an inherently collaborative enterprise connecting authors, nonprofit publishers, academic institutions, research libraries, and research funders in the common goal of maximizing access to critical research.

Journal of Wildlife Diseases, 44(3), 2008, pp. 716 720 # Wildlife Disease Association 2008 Effect of Temperature on Host Response to Batrachochytrium dendrobatidis Infection in the Mountain Yellow-legged Frog (Rana muscosa) Sara E. Andre, 1,4 John Parker, 2 and Cheryl J. Briggs 31 School of Veterinary Medicine, University of California, Davis, California 95616, USA; 2 Office of Laboratory and Animal Care, University of California, Berkeley, California 94720, USA; 3 Department of Ecology, Evolution and Marine Biology, University of California, Santa Barbara, California 93106-9610, USA; 4 Corresponding author (email: sandre@ucdavis.edu) ABSTRACT: The pathogenic chytrid fungus Batrachochytrium dendrobatidis, which causes the disease chytridiomycosis, has been implicated in declines of amphibian populations throughout the world, including declines and extinctions of local populations of mountain yellow-legged frogs, Rana muscosa, in the California Sierra Nevada. Previous studies have shown B. dendrobatidis achieves its maximum growth rate in culture in the temperature range of 17 25 C, and exposure to very high temperatures can clear frogs of B. dendrobatidis infection. Here we present the results of a laboratory experiment in which experimentally infected R. muscosa tadpoles were followed through metamorphosis at temperatures of 17 and 22 C. All infected animals developed clinical disease within a similar time frame. However, frogs housed at 22 C exhibited a significantly lower mortality than those housed at 17 C. Within 35 days after metamorphosis, 50% of the frogs housed at 22 C died, while 95% of the frogs housed at 17 C died. Clinical signs subsided in the surviving frogs at 22 C, despite persistent infection. Because both temperatures are within the optimal thermal range for growth of B. dendrobatidis, we propose that the difference in outcome indicates the effect of temperature on the host s resistance to chytridiomycosis, rather than an effect on the fungus alone. Key words: Amphibian, amphibian chytrid fungus, Batrachochytrium dendrobatidis, chytridiomycosis, mortality, Rana muscosa, temperature. Chytridiomycosis, the disease caused by the chytrid fungus Batrachochytrium dendrobatidis, has been implicated as the cause of sudden declines in several frog populations. Infected frogs have been found in Australia, Europe, Africa, New Zealand, Central America, South America, and North America (Berger, 1998; Muths et al., 2003; Lips et al., 2006). The mountain yellow-legged frog, Rana muscosa, which occurs only in high elevation areas of the California Sierra Nevada Mountains in western North America, has experienced recent population declines and local extinctions due to mortality caused by B. dendrobatidis (Rachowicz et al., 2006). Batrachochytrium dendrobatidis infection is restricted to the outermost portion of the epidermis, and disease results when the fungal burden surpasses the tolerance of the host. In general, larval frogs are not susceptible to clinical disease due to their lack of dermal keratin. However, tadpoles of Rana spp. are equipped with minimal amounts of keratin in their mouthparts, a state which provides a focal site for B. dendrobatidis infection with no effect on activity or mortality. One exception is boreal toad (Bufo boreus) tadpoles, which have shown increased mortality after Batrachochytrium exposure (Blaustein et al., 2005). The subclinical infection of tadpoles provides a means for autoinfection at metamorphosis (Marantelli et al., 2004). In many species, B. dendrobatidis infection results in death of subadults and adults; however, the outcome of infection varies between populations and individuals. Batrachochytrium dendrobatidis has been demonstrated to be a highly virulent primary pathogen in some captive and wild populations, yet causes only subclinical to transient infection in other populations (Berger, 1998; Muths et al., 2003; Lips et al., 2006; Rachowicz et al., 2006). Given B. dendrobatidis low genetic variability, geographic structuring, and host specificity (Morehouse et al., 2003), this variation in pathogenicity may reflect the 716

SHORT COMMUNICATIONS 717 influence of both environmental and host factors. The effect of temperature on B. dendrobatidis has recently received a great deal of attention (Pounds et al., 2006). In pure culture, B. dendrobatidis has the highest growth rate at temperatures between 17 to 25 C, but can grow and reproduce at temperatures spanning 4 to 25 C, allowing it to survive in overwintering hosts (Johnson and Speare, 2003; Piotrowski et al., 2004). In some species, infection prevalence has been found to be highest during cool temperature periods (Berger et al., 2004; Woodhams and Alford, 2005; Kriger and Hero, 2007). Carey et al. (2006) found that survival time after experimental B. dendrobatidis infection in boreal toads did not differ at temperatures between 12 C and 23 C. In another experiment with great barred frogs (Mixophyes fasciolatus), Berger et al. (2004) found all frogs exposed at 17 C and 23 C died following exposure to B. dendrobatidis, but half of the individuals exposed at 27 C survived. In addition, elevated temperatures of 27 C and 37 C have been shown to cure chytridiomycosis in certain species of frogs (Woodhams et al., 2003; Berger et al., 2004). In this study, we investigate the effect of B. dendrobatidis on mountain yellowlegged frogs (R. muscosa) at two temperatures that are within the optimal thermal range for B. dendrobatidis growth in culture, as well as within the thermal range typically experienced by R. muscosa (Bradford, 1984). Sixty R. muscosa tadpoles, approximately 1 yr of age and of undetermined sex (reared from egg masses collected in 2002 from Kings Canyon National Park, California, USA), were housed in the ectotherm facility at University of California, Berkeley (UCB), Berkeley, California, USA. The UCB campus is fully accredited by the Association for Assessment and Accreditation of Laboratory Animal Care International, and these animals were covered under a protocol approved by the UCB Institutional Animal Care and Use Committee. Experimental infection was achieved, several months prior to this experiment, using the LJR089 strain of B. dendrobatidis cultured in 2002 from an infected R. muscosa from Sequoia National Park, California. Inoculation occurred following the protocol described by Rachowicz and Briggs (2007), in which 20-l tadpole tanks filled with 12 l of water were inoculated with approximately 1310 7 zoospores (determined by hemocytometer counts). Over a period of 3 wk, each tank was inoculated a total of 15 times. All infected tadpoles were housed at 17 C during the inoculation period and during the following 2 months. Upon reaching Gosner stage 41, experimentally infected tadpoles and uninfected controls were divided into two temperature status treatments consisting of 20 experimentally infected individuals and 10 uninfected at each temperature (17 or 22 C). Animals were individually housed in 5-l fiberglass aquaria and maintained in static dechloraminated water that was changed biweekly. Development was monitored and recorded four times a week using stages based on Gosner s anuran embryo staging tables (Gosner, 1960). Aquaria water levels were uniformly set according to the Gosner stage of the individual animal, and twice a week animals were moved to freshly prepared tanks. Prior to Gosner stage 42, tadpoles were kept in fully aquatic tanks. From Gosner stage 42 through 43, metamorphs were kept in tanks with approximately 2.5 cm of water and a folded paper towel. Upon entering Gosner stage 44, metamorphs were placed in tanks with only 1.2 cm of water. Tadpoles were fed rabbit pellets, and postmetamorphic animals were provided live crickets. Cricket consumption was monitored and recorded throughout the experiment. Infection status was confirmed via skin-scraping cytology prior to the start of the experiment and at various time points thereafter. Likewise, controls

718 JOURNAL OF WILDLIFE DISEASES, VOL. 44, NO. 3, JULY 2008 were confirmed to lack detectable levels of pathogen prior to, and throughout, the experiment. The skin scraping technique (Drake et. al., 2007) involved using a wooden applicator stick or the blunt side of a scalpel to scrape epithelial cells from either the jaw sheaths or tooth rows of tadpoles, or from the ventral surface of the feet, legs, and abdomen of postmetamorphic frogs. The cells were spread onto a drop of water on a microscope slide and examined for the presence of B. dendrobatidis sporangia using a compound microscope at 100 4003 magnification. Animals were euthanized upon reaching the experimental endpoint, defined as marked obtundation, non-ambulatory, lacking of righting response, or death. The Kaplan-Meier method of survival function estimation was used to compare rates of death between groups, and a logrank test was used to compare survival functions for equality. The Cox proportional-hazards regression model was used to estimate hazard rate ratios (HRR) and 95% confidence intervals (95% CI) comparing group effects. Any P values,0.05 were considered statistically significant. Sixty frogs were initially included in the study. Two animals (one infected animal at 22 C and one uninfected control at 17 C) were excluded from the study due to unrelated mortality as tadpoles. One of the infected frogs in the 22 C room was euthanized 9 days after entering Gosner stage 45 due to an extreme hind limb edema believed to be unrelated to the fungal infection. In all, the median survival time in infected frogs was 25 days, and the estimated survival probability of infected frogs 35 days after entering Gosner stage 45 was 26%. This survival was significantly less (P,0.001) than in uninfected frogs, which experienced no postmetamorphic mortality at either temperature. Among the infected frogs (n539), there was a significant difference in mortality between the two temperature groups (P50.0036; Fig. 1). At 17 C, only 5% of the infected FIGURE 1. Survival probabilities of Rana muscosa infected with Batrachochytrium dendrobatidis at 17 and 22 C as a function of the number of days postmetamorphosis (onset of Gosner stage 45). Some frogs were censored due to death from other causes, or for remaining alive at the end of the experiment. No uninfected frogs died from chytrid infection (data not shown). frogs survived, the last death occurring on day 35; at 22 C, 50% of the infected frogs survived, the last death occurring on day 32. The rate of death among infected frogs in the higher temperature group was approximately one fifth that of the rate in the lower temperature groups (HRR5 0.20, 95% CI50.086 0.48). Excessive shedding was observed in all infected animals, at both temperatures, as compared to controls. Skin sloughed from infected animals appeared to be in much smaller pieces than the sloughed skin observed from healthy animals undergoing ecdysis. Other clinical signs of disease, including inappetence, lethargy, and reduced responsiveness, were also noted in all infected animals, but appeared, subjectively, more pronounced at the cooler temperature. Animals that survived beyond 35 days postmetamorphosis at 22 C regained their appetite and responsiveness and subsequently recovered from the disease, despite the persistence of infection. The single survivor at 17 C remained anorectic and unresponsive for the duration of the study.

SHORT COMMUNICATIONS 719 The positive effects of higher ambient temperature on survival or recovery of frogs infected with B. dendrobatidis has previously been established (Woodhams et al., 2003; Berger et al., 2004). However, in those reports, these effects were demonstrated only when temperatures exceeded those considered optimal to sustain B. dendrobatidis growth. Consequently, the observed attenuation and resolution of disease in those reports may have been due to the elevated temperature s direct effect on the pathogen s survivability (Berger et al., 2004). Providing that optimal growth of B. dendrobatidis in culture correlates with its capacity to produce disease, and all other factors are considered equal, the temperatures employed in this study should have had no effect on the pathogenesis. Thus, the difference in pathogenicity demonstrated in this study is attributable to an increased capability of the host to contend with infection. These results suggest the thermal optimum for B. dendrobatidis growth in culture may not necessarily determine its impact within particular amphibian populations. Thanks to P. Kass, who provided invaluable statistical advice. This work was funded by Ecology of Infectious Diseases grants from NIH (R01 ES12067) and NSF (EF- 0723563) provided to Cheryl J. Briggs. LITERATURE CITED BERGER, L., R. SPEARE,P.DASZAK,D.E.GREEN,A.A. CUNNINGHAM, C.L.GOGGIN, R.SLOCOMBE, M.A. RAGAN, A.D.HYATT, K.R.MCDONALD, H.B. HINES, K. R. LIPS, G. MARANTELLI, AND H. PARKES. 1998. Chytridiomycosis causes amphibian mortality associated with population declines in the rain forests of Australia and Central America. Proceedings of the National Academy of Sciences 95: 9031 9036.,, H. B. HINES, G.MARANTELLI, A.D. HYATT, K. R. MCDONALD, L. F. SKERRATT, V. OLSEN, J.M.CLARKE, G.GILLESPIE, M.MAHONY, N. SHEPPARD, C. WILLIAMS, AND M. J. TYLER. 2004. Effect of season and temperature on mortality in amphibians due to chytridiomycosis. Australian Veterinary Journal 82: 434 439. BLAUSTEIN, A. R., J. M. ROMANSIC, E. A. SCHEESSELE, B. A. HAN, A. P. PESSIER, AND J. E. LONGCORE. 2005. Interspecific variation in susceptibility of frog tadpoles to the pathogenic fungus Batracbochytrium dendrobatidis. Conservation Biology 19: 1460 1468. BRADFORD, D. F. 1984. Temperature modulation in a high-elevation amphibian, Rana muscosa. Copeia 4: 966 976. CAREY, C., J. E. BRUZGUL, L. J. LIVO, M. L. WALLING, K. A. KUEHL, B. F. DIXON, A. P. PESSIER, R. A. ALFORD, AND K. B. ROGERS. 2006. Experimental exposures of boreal toads (Bufo boreas) to a pathogenic chytrid fungus (Batrachochytrium dendrobatidis). EcoHealth 3: 5 21. DRAKE, D. L., R. ALTIG, J. B. GRACE, AND S. C. WALLS. 2007. Occurrence of oral deformities in larval anuran. Copeia 2007: 449 458. GOSNER, K. L. 1960. A simplified table for staging anuran embryos and larvae. Herpetologica 16: 183 190. JOHNSON, M. L., AND R. SPEARE. 2003. Survival of Batrachochytrium dendrobatidis in water: Quarantine and disease control implications. Emerging Infectious Diseases 9: 922 925. KRIGER, K. M., AND J. M. HERO. 2007. Large-scale seasonal variation in the prevalence and severity of chytridiomycosis. Journal of Zoology (London) 271: 352 359. LIPS, K. R., F. BREM, R. BRENES, J. D. REEVE, R. A. ALFORD, J. VOYLES, C. CAREY, L. LIVO, A. P. PESSIER, AND J. P. COLLINS. 2006. Emerging infectious disease and the loss of biodiversity in a Neotropical amphibian community. Proceedings of the National Academy of Sciences of the United States of America 103: 3165 3170. MARANTELLI, G., L. BERGER, R. SPEARE, AND L. KEEGAN. 2004. Distribution of the amphibian chytrid Batrachochytrium dendrobatidis and keratin during tadpole development. Pacific Conservation Biology 10: 173 179. MOREHOUSE, E. A., T. Y. JAMES, A. R. D. GANLEY, R. VILGALYS, L. BERGER, P. J. MURPHY, AND J. E. LONGCORE. 2003. Multilocus sequence typing suggests the chytrid pathogen of amphibians is a recently emerged clone. Molecular Ecology 12: 395 403. MUTHS, E., P. S. CORN, A. P. PESSIER, AND D. E. GREEN. 2003. Evidence for disease-related amphibian decline in Colorado. Biological Conservation 110: 357 365. PIOTROWSKI, J. S., S. L. ANNIS, AND J. E. LONCORE. 2004. Physiology of Batrachochytrium dendrobatidis, a chytrid pathogen of amphibians. Mycologia 96: 9 15. POUNDS, J. A., M. R. BUSTAMANTE, L.A.COLOMA, J.A. CONSUEGRA, M.P.L.FOGDEN, P.N.FOSTER, E. LA MARCA, K.L.MASTERS, A.MERINO-VITERI, R. PUSCHENDORF, S. R. RON, G. A. SANCHEZ- AZOFEIFA, C. J. STILL, AND B. E. YOUNG. 2006.

720 JOURNAL OF WILDLIFE DISEASES, VOL. 44, NO. 3, JULY 2008 Widespread amphibian extinctions from epidemic disease driven by global warming. Nature 439: 161 167. RACHOWICZ, L. J., AND C. J. BRIGGS. 2007. Quantifying the disease transmission function effects of density on Batrachochytrium dendrobatidis transmission in the mountain Yellow-legged frog Rana muscosa. Journal of Animal Ecology 76: 711 721., R. A. KNAPP, J.A.T.MORGAN, M.J.STICE, V. T. VREDENBURG, J. M. PARKER, AND C. J. BRIGGS. 2006. Emerging infectious disease as a proximate cause of amphibian mass mortality. Ecology 87: 1671 1683. WOODHAMS, D. C., AND R. A. ALFORD. 2005. Ecology of chytridiomycosis in rainforest stream frog assemblages of tropical Queensland. Conservation Biology 19: 1449 1459.,, AND G. MARANTELLI. 2003. Emerging disease of amphibians cured by elevated body temperature. Diseases of Aquatic Organisms 55: 65 67. Received for publication 28 May 2007.