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Presence of Ranavirus and Chytrid Fungus in Lithobates sphenocephalus in Long and Short Hydroperiod Wetlands Shaina Carrington 1,2 , David Scott 1 , Megan Winzeler 1 , Austin Coleman 1 , Carlos Tapia 1,3 , and Stacey Lance 1 1 UGA Savannah River Ecology Laboratory, Aiken, SC, 2 Virginia Polytechnic Institute and State University, Blacksburg, VA, and 3 University of Central Florida, Orlando, FL Background/Justification Objectives Results Methods Predictions Literature References Batrachochytrium dendrobatidis (chytrid or Bd) and Ranavirus are two pathogens linked to global amphibian declines 1,2 Chytrid Fungus(Bd): Has been detected in 56 countries 3 Directly transmitted through physical contact Colonizes the keratinized epidermis and mouthparts of amphibians Disrupts osmoregulation, causing toxin release and resulting in death At Savannah River Site: Been present since the 1970s, but at low frequencies 4 Strongly affected seasonally 5 Recent Study Shows: Bd more prevalent in contaminated and long hydroperiod wetlands The prevalence has increased since the 1970s Ranavirus: Has been detected on 5 continents Transmitted through ingestion and physical contact 6 Culminates in organ necrosis causing massive hemorrhaging and death Infects amphibians, reptiles, and fish 7 At Savannah River Site: Prevalence is 4 times greater than Bd Strongly associated with life stages and affected seasonally Recent Study Shows: Ranavirus more prevalent in long hydroperiod wetlands No significant difference in the prevalence of the virus in contaminated vs. uncontaminated wetlands Ranavirus is common in southern leopard frogs Problem with recent study: Only examined 12 wetlands All contaminated wetlands were long hydroperiods Didn’t have the same species from each study site Solution (my study): Examine more wetlands Only include uncontaminated reference wetlands Use only one species from each study site To determine: The current prevalence of Bd and ranavirus in southern leopard frogs on the SRS The prevalence of Bd and ranavirus in long and short hydroperiod wetlands Whether disease loads differ among individuals from long and short hydroperiod wetlands Based on prior studies: Long hydroperiod wetlands should have higher disease prevalence compared to the short Ranavirus should be at higher prevalence than Bd d Study Area: Savannah River Site near Aiken, SC 25 wetlands sampled for southern leopard frogs 11 short hydroperiod wetlands 14 long hydroperiod wetlands 280 tissue samples from tadpoles (145 from long and 135 from short) Map Key: Long Hydroperiod Short Hydroperiod Experimental Design: Active dip-netting in both wetland types Minnow trapping to supplement captures Tail clipping to collect tissue for DNA DNA Bead Beater Extraction Protocol Figure 3. SRS study sites Quantitative Sampling: qPCR using Taqman primer/probe protocol Samples run in triplicate 100, 10, 1, and 0.1 serial dilution of fungal standards 10 6 -10 1 serial dilution of virus standards Samples were analyzed using BioRad CFX Manager Figure 1. Bd has been associated with dramatic population declines worldwide Figure 2. Ranaviruses have been linked to mass mortality events in amphibians Figures 6. Active dip-netting in long hydroperiod wetlands Figure 7. Processing tadpoles Figure 8. Prep-qPCR Figure 9. PCR machine No positives for either pathogens Both hypotheses rejected Figure 10. Amplification curve showing the relationship between qPCR cycle number and relative fluorescence. In this figure the standards are shown. Figure 11. Standard curve, showing the relationship between the starting quantity of DNA and the qPCR cycle number where more than background fluorescence is observed (Cq). Conclusions/Future Implications Conclusions: Surprising because the recent study showed 24% positive for Bd and 32% positive for ranavirus for this species The recent study was tested throughout February-July 2013, while my study was tested throughout March-May 2015 Chytrid Temperature/Seasonal Tolerance: More prevalent in the winter Bd does not grow at water temperatures above 28°C 8 Ranavirus Temperature/Seasonal Tolerance: More prevalent in autumn and decreasing throughout the rest of the seasons 9 Acknowledgements We would like to thank the Lance Lab, REU program participants, Melissa Pilgrim, Tracey Tuberville, J Vaun McArthur, and SREL. Also, thank you to National Science Foundation, Department of Energy, and Savannah River Site. 1. Berger L, Speare R, Daszak P, Green DE, Cunningham AA, Goggin CL, et al. Chytridiomycosis causes amphibian mortality associated with population declines in the rain forests of Australia and Central America. Proc Natl Acad Sci USA. 1998;95: 9031-9036. 2. Green DE, Converse KA, Schrader AK. Epizootiology of sixty-four amphibian morbidity and mortality events in the USA, 1996-2001. Ann New York Acad Sci. 2002;5: 323-339. 3. Olson DH, Anaensen DM, Ronnenberg KL, Powell CI, Walker SF, Biebly J, et al. Mapping the global emergence of Batrachochytrium dendrobatidis, the amphibian chytrid fungus. PLos One. 2013;8. 4. Daszak AP, Scott DE, Kilpatrick AM, Faggioni C, Gibbons JW, Porter D. Amphibian population declines at Savannah River Site are linked to climate, not chytridiomycosis. Ecology. 2005;86: 3232-3237 5. Love CN, Winzeler ME, Beasley R, Scott DE, Nuziata SO, Lance SL. Patterns of amphibian disease prevalence across contaminated and uncontaminated wetlands on the Savannah River Site, S.C. In Review. 6. Miller D, Gray M, Storfer A. Ecopathology of ranaviruses infecting amphibians. Viruses. 2011;3: 2351-73 7. Gray MJ, Miller DL, Hoverman JT. Ecology and pathology of amphibian ranaviruses. Dis Aquat Organ. 2009;87:243-266 8. Peterson JD, Wood MB, Hopkins WA., Unrine JM, and Mendonca MT. Prevalence of Batrachochytrium dendrobatidis in American bullfrog and southern leopard frog larvae from wetlands on the Savannah River Site, South Carolina. Journal of wildlife Diseases. 2007;43(3): 450-460 9. Hoverman JT, Gary MJ, Miller DL, Hailslip NA. Widespread occurrence of ranavirus in pond-breeding amphibian populations. International Association for Ecology and Health. 2011. Figure 5. Ellenton Bay- long hydroperiod wetland Figure 4. Rainbow Bay- short hydroperiod wetland Future Implications: Further research should examine the patterns in disease prevalence in different hydroperiod Figure 12. Southern leopard frog (L. sphenocephalus) metamorph wetlands. Each hydroperiod type should be examined to understand how seasonal changes affect the pathogens. Shifting disease patterns may accompany climate change. Threshold Fluorescence Positive Sample

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  • Presence of Ranavirus and Chytrid Fungus in Lithobates sphenocephalus in Long and Short Hydroperiod Wetlands

    Shaina Carrington1,2, David Scott1, Megan Winzeler1, Austin Coleman1, Carlos Tapia1,3, and Stacey Lance1

    1UGA Savannah River Ecology Laboratory, Aiken, SC, 2Virginia Polytechnic Institute and State University, Blacksburg, VA, and 3University of Central Florida, Orlando, FL

    Background/Justification

    Objectives

    Results Methods

    Predictions Literature References

    Batrachochytrium dendrobatidis (chytrid or Bd) and Ranavirus aretwo pathogens linked to global amphibian declines1,2

    Chytrid Fungus(Bd):

    Has been detected in 56 countries3

    Directly transmitted throughphysical contact

    Colonizes the keratinizedepidermis and mouthparts ofamphibians

    Disrupts osmoregulation, causing toxin release and resulting indeath

    At Savannah River Site: Been present since the 1970s, but at low frequencies4

    Strongly affected seasonally5

    Recent Study Shows: Bd more prevalent in contaminated and long

    hydroperiod wetlands The prevalence has increased since the 1970s

    Ranavirus:

    Has been detected on 5 continents Transmitted through ingestion and

    physical contact6

    Culminates in organ necrosiscausing massive hemorrhaging anddeath

    Infects amphibians, reptiles, and fish7

    At Savannah River Site: Prevalence is 4 times greater than Bd Strongly associated with life stages and affected

    seasonally

    Recent Study Shows: Ranavirus more prevalent in long hydroperiod wetlands No significant difference in the prevalence of the virus in

    contaminated vs. uncontaminated wetlands Ranavirus is common in southern leopard frogs

    Problem with recent study:

    Only examined 12 wetlands All contaminated wetlands were long hydroperiods Didn’t have the same species from each study site

    Solution (my study):

    Examine more wetlands Only include uncontaminated reference wetlands Use only one species from each study site

    To determine:

    The current prevalence of Bd and ranavirus in southern leopard frogs on the SRS

    The prevalence of Bd and ranavirus in long and short hydroperiod wetlands

    Whether disease loads differ among individuals from long and short hydroperiod wetlands

    Based on prior studies:

    Long hydroperiod wetlands should have higher disease prevalence compared to the short

    Ranavirus should be at higher prevalence than Bd

    d

    Study Area: Savannah River Site near Aiken, SC

    25 wetlands sampled for southern leopard frogs 11 short hydroperiod wetlands 14 long hydroperiod wetlands

    280 tissue samples from tadpoles (145 from long and 135 from short)

    Map Key:

    Long Hydroperiod

    Short Hydroperiod

    Experimental Design:

    Active dip-netting in both wetland types Minnow trapping to supplement captures Tail clipping to collect tissue for DNA DNA Bead Beater Extraction Protocol

    Figure 3. SRS study sites

    Quantitative Sampling:

    qPCR using Taqman primer/probe protocol Samples run in triplicate 100, 10, 1, and 0.1 serial dilution of fungal standards 106-101 serial dilution of virus standards Samples were analyzed using BioRad CFX Manager

    Figure 1. Bd has been associated with dramatic population declines worldwide

    Figure 2. Ranaviruses have been linked to mass mortality events in amphibians

    Figures 6. Active dip-netting in long hydroperiod wetlands

    Figure 7. Processing tadpoles

    Figure 8. Prep-qPCR Figure 9. PCR machine

    No positives for either pathogens Both hypotheses rejected

    Figure 10. Amplification curve showing the relationship between qPCR cycle number and relative fluorescence. In this figure the standards are shown.

    Figure 11. Standard curve, showing the relationship between the starting quantity of DNA and the qPCR cycle number where more than background fluorescence is observed (Cq).

    Conclusions/Future Implications

    Conclusions:

    Surprising because the recent study showed 24% positive for Bd and 32% positive for ranavirus for this species

    The recent study was tested throughout February-July 2013, while my study was tested throughout March-May 2015

    Chytrid Temperature/Seasonal Tolerance:

    More prevalent in the winter Bd does not grow at water temperatures above 28°C8

    Ranavirus Temperature/Seasonal Tolerance:

    More prevalent in autumn and decreasing throughout the rest of the seasons9

    Acknowledgements

    We would like to thank the Lance Lab, REU program participants, Melissa Pilgrim, Tracey Tuberville, J VaunMcArthur, and SREL. Also, thank you to National Science Foundation, Department of Energy, and Savannah River Site.

    1. Berger L, Speare R, Daszak P, Green DE, Cunningham AA, Goggin CL, et al. Chytridiomycosis causes amphibian mortality associated with population declines in the rain forests of Australia and Central America. Proc Natl Acad Sci USA. 1998;95: 9031-9036.

    2. Green DE, Converse KA, Schrader AK. Epizootiology of sixty-four amphibian morbidity and mortality events in the USA, 1996-2001. Ann New York Acad Sci. 2002;5: 323-339.3. Olson DH, Anaensen DM, Ronnenberg KL, Powell CI, Walker SF, Biebly J, et al. Mapping the global emergence of Batrachochytrium dendrobatidis, the amphibian

    chytrid fungus. PLos One. 2013;8.4. Daszak AP, Scott DE, Kilpatrick AM, Faggioni C, Gibbons JW, Porter D. Amphibian population declines at Savannah River Site are linked to climate, not chytridiomycosis. Ecology.

    2005;86: 3232-32375. Love CN, Winzeler ME, Beasley R, Scott DE, Nuziata SO, Lance SL. Patterns of amphibian disease prevalence across contaminated and uncontaminated wetlands on the

    Savannah River Site, S.C. In Review.6. Miller D, Gray M, Storfer A. Ecopathology of ranaviruses infecting amphibians. Viruses. 2011;3: 2351-73 7. Gray MJ, Miller DL, Hoverman JT. Ecology and pathology of amphibian ranaviruses. Dis Aquat Organ. 2009;87:243-2668. Peterson JD, Wood MB, Hopkins WA., Unrine JM, and Mendonca MT. Prevalence of Batrachochytrium dendrobatidis in American bullfrog and southern leopard frog larvae

    from wetlands on the Savannah River Site, South Carolina. Journal of wildlife Diseases. 2007;43(3): 450-4609. Hoverman JT, Gary MJ, Miller DL, Hailslip NA. Widespread occurrence of ranavirus in pond-breeding amphibian populations. International Association for Ecology and Health.

    2011.

    Figure 5. Ellenton Bay- long hydroperiod wetland

    Figure 4. Rainbow Bay- short hydroperiod wetland

    Future Implications:

    Further research should examine the patterns in disease prevalence in different hydroperiod

    Figure 12. Southern leopard frog (L. sphenocephalus) metamorph

    wetlands. Each hydroperiod type should be examined to understand how seasonal changes affect the pathogens. Shifting disease patterns may accompany climate change.

    Threshold Fluorescence

    Positive Sample