Table 1 Chilean anurans studied for Batrachochytrium dendrobatidis (Bd) infection from 2008 to 2018.
Species | Ecology | Negative | Positive | Sample size | Proportion of infection (%) | 95% CI | Median ZE | IUCN |
|---|---|---|---|---|---|---|---|---|
Alsodes australis | T | 13 | 0 | 13 | 0 | 0–22.8 | 0 | DD |
Alsodes barrioi | T | 27 | 0 | 27 | 0 | 0–12.5 | 0 | EN |
Alsodes coppingeri | T | 2 | 0 | 2 | 0 | 0–65.8 | 0 | DD |
Alsodes nodosus | A | 27 | 5 | 32 | 15.6 | 6.9–31.8 | 166 | NT |
Alsodes tumultuosus | A | 47 | 21 | 68 | 30.9 | 21.2–42.6 | 1302 | VU |
Alsodes valdiviensis | T | 11 | 9 | 20 | 45.0 | 25.8–65.8 | 13 | EN |
Alsodes verrucosus | T | 3 | 0 | 3 | 0 | 0–56.2 | 0 | EN |
Atelognathus salai | A | 0 | 4 | 4 | 100 | 51.0–100 | 419 | LC |
Batrachyla antartandica | A | 143 | 21 | 164 | 12.8 | 8.5–18.8 | 62 | LC |
Batrachyla leptopus | A | 66 | 2 | 68 | 2.9 | 0.8–10.1 | 1.6 | LC |
Batrachyla taeniata | A | 83 | 5 | 88 | 5.7 | 2.5–12.6 | 318 | LC |
Calyptocephalella gayi | A | 281 | 150 | 431 | 34.8 | 30.5–39.4 | 436 | VU |
Chaltenobatrachus grandisonae | A | 22 | 8 | 30 | 26.7 | 14.2–44.5 | 621 | LC |
Eupsophus altor | T | 5 | 0 | 5 | 0 | 0–43.5 | 0 | NE |
Eupsophus calcaratus | T | 87 | 12 | 99 | 12.1 | 7.1–20.0 | 53 | LC |
Eupsophus contulmoensis | T | 30 | 7 | 37 | 18.9 | 9.5–34.2 | 30 | EN |
Eupsophus emiliopugini | A | 17 | 1 | 18 | 5.6 | 0.3–25.8 | 6 | LC |
Eupsophus migueli | T | 1 | 0 | 1 | 0 | 0–94.9 | 0 | EN |
Eupsophus nahuelbutensis | T | 104 | 5 | 109 | 4.6 | 2.0–10.3 | 55 | EN |
Eupsophus roseus | A | 35 | 4 | 39 | 10.3 | 4.1–23.6 | 86 | LC |
Eupsophus septentrionalis | A | 10 | 2 | 12 | 16.7 | 4.7–44.8 | 33 | DD |
Eupsophus vertebralis | T | 9 | 0 | 9 | 0 | 0–29.9 | 0 | LC |
Hylorina sylvatica | T | 6 | 3 | 9 | 33.3 | 12.1–64.6 | 222 | LC |
Nannophryne variegata | T | 3 | 0 | 3 | 0 | 0–56.2 | 0 | LC |
Pleurodema bufonina | A | 98 | 6 | 104 | 5.8 | 2.7–12 | 154 | LC |
Pleurodema thaul | A | 737 | 266 | 1003 | 26.5 | 23.9–29.3 | 115 | LC |
Rhinella arunco | T | 4 | 11 | 15 | 73.3 | 48.1–89.1 | 61 | NT |
Rhinella atacamensis | T | 26 | 0 | 26 | 0 | 0–12.9 | 0 | VU |
Rhinella spinulosa | T | 45 | 0 | 45 | 0 | 0–7.9 | 0 | LC |
Rhinoderma darwinii | T | 788 | 14 | 802 | 1.8 | 1.0–2.9 | 1170 | EN |
Telmatobius chusmisensis | A | 11 | 24 | 35 | 68.6 | 52.0–81.5 | 1830 | EN |
Telmatobius dankoi | A | 49 | 0 | 49 | 0 | 0–7.3 | 0 | CR |
Telmatobius fronteriensis | A | 14 | 0 | 14 | 0 | 0–21.5 | 0 | CR |
Telmatobius marmoratus | A | 31 | 0 | 31 | 0 | 0–11.0 | 0 | EN |
Telmatobius pefauri | A | 19 | 16 | 35 | 45.7 | 30.5–61.8 | 28 | CR |
Telmatobius peruvianus | A | 5 | 6 | 11 | 54.6 | 28.0–78.7 | 2 | VU |
Telmatobius halli | A | 7 | 0 | 7 | 0 | 0–35.4 | 0 | DD |
Telmatobius vilamensis | A | 13 | 0 | 13 | 0 | 0–22.8 | 0 | CR |
Telmatobufo bullocki | A | 3 | 0 | 3 | 0 | 0–56.2 | 0 | EN |
Xenopus laevis | A | 388 | 172 | 560 | 30.7 | 27.0–34.7 | 400 | LC |
