<?xml version='1.0' encoding='utf-8'?>
<oai_dc:dc xmlns:dc="http://purl.org/dc/elements/1.1/" xmlns:oai_dc="http://www.openarchives.org/OAI/2.0/oai_dc/" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance" xsi:schemaLocation="http://www.openarchives.org/OAI/2.0/oai_dc/ http://www.openarchives.org/OAI/2.0/oai_dc.xsd">
  <dc:contributor>Rebecca M. McCaffery</dc:contributor>
  <dc:contributor>Ana V. Longo</dc:contributor>
  <dc:contributor>Kelly R. Zamudio</dc:contributor>
  <dc:contributor>Karen R. Lips</dc:contributor>
  <dc:creator>Graziella Vittoria DiRenzo</dc:creator>
  <dc:date>2025</dc:date>
  <dc:description>&lt;p&gt;&lt;span&gt;Emerging infectious diseases can cause rapid, widespread host mortality, and the lack of demographic data before and after pathogen emergence complicates understanding mechanisms of host persistence. This challenge is further compounded by environmental conditions that influence host behavior, while driving pathogen growth and virulence. These interactions create complex disease outcomes that hinder predictions of when and how hosts endure pathogen outbreaks. Here, we analyzed 10 years of capture-mark-recapture data (2000–2014) spanning wet and dry seasons for male&amp;nbsp;&lt;/span&gt;&lt;i&gt;Espadarana prosoblepon&lt;/i&gt;&lt;span&gt;&amp;nbsp;in El Copé, Panama, encompassing a period before (2000–2004) and after (2010–2014) a&amp;nbsp;&lt;/span&gt;&lt;i&gt;Batrachochytrium dendrobatidis&lt;/i&gt;&lt;span&gt;&amp;nbsp;(&lt;/span&gt;&lt;i&gt;Bd&lt;/i&gt;&lt;span&gt;) outbreak using Jolly-Seber models. We found that post-&lt;/span&gt;&lt;i&gt;Bd&lt;/i&gt;&lt;span&gt;&amp;nbsp;male&amp;nbsp;&lt;/span&gt;&lt;i&gt;E. prosoblepon&lt;/i&gt;&lt;span&gt;&amp;nbsp;population size (range in mean population size among primary periods = 136–225 individuals) was similar to pre-&lt;/span&gt;&lt;i&gt;Bd&lt;/i&gt;&lt;span&gt;&amp;nbsp;population size (range in mean population size among primary periods = 201–242 individuals). Pre-&lt;/span&gt;&lt;i&gt;Bd&lt;/i&gt;&lt;span&gt;, average monthly survival probability in the wet season was 0.93 (95% credible interval [CI] = 0.90–0.96). Post-&lt;/span&gt;&lt;i&gt;Bd&lt;/i&gt;&lt;span&gt;, uninfected individuals had survival probability higher in the wet season (mean = 0.97; [95% CI = 0.95–0.98]) than the dry season (mean = 0.90 [95% CI = 0.84–0.94]), while survival probability for infected individuals decreased as a function of&amp;nbsp;&lt;/span&gt;&lt;i&gt;Bd&lt;/i&gt;&lt;span&gt;&amp;nbsp;infection intensity. Pre-&lt;/span&gt;&lt;i&gt;Bd&lt;/i&gt;&lt;span&gt;, mean monthly per-capita entry probability was 0.07 (95% CI = 0.05–0.10), and post-&lt;/span&gt;&lt;i&gt;Bd&lt;/i&gt;&lt;span&gt;, mean monthly per-capita entry probability was 0.06 (95% CI = 0.00–0.10). Lastly, infection probability during the wet season was lower (mean = 0.04 [95% CI = 0.03–0.05]) than the dry season (mean = 0.10 [95% CI = 0.05–0.15]), and recovery probability during the wet season was lower (mean = 0.19 [95% CI = 0.11–0.28]) than the dry season (mean = 0.54 [95% CI = 0.20–0.88]). Our findings suggest that survival probabilities of uninfected individuals, as well as per-capita entry probabilities, are similar pre- and post-&lt;/span&gt;&lt;i&gt;Bd&lt;/i&gt;&lt;span&gt;, leading to a stable and similar sized pre-&lt;/span&gt;&lt;i&gt;Bd&lt;/i&gt;&lt;span&gt;&amp;nbsp;population. These results contribute to understanding disease dynamics and tropical amphibian ecology.&lt;/span&gt;&lt;/p&gt;</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.1002/ecs2.70350</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>Ecological Society of America</dc:publisher>
  <dc:title>Similar population dynamics before and after a chytridiomycosis outbreak in a tropical riparian amphibian species</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>