Skip to main content
. Author manuscript; available in PMC: 2019 Mar 1.
Published in final edited form as: J Anim Ecol. 2017 Nov 27;87(2):489–499. doi: 10.1111/1365-2656.12769

Fig. 2.

Fig. 2

Methods to determine the relationships among atrazine exposure, corticosterone levels, host-associated gut microbiota, and Bd infection risk in Cuban tree frogs. Superscript letters represent the timing of treatment exposure and sampling effort: aOn day one, tadpoles were placed in tanks with water that was treated experimentally with atrazine and/or metryapone using a 2×2 factorial design (8 tadpoles per tank). bOn day six, tadpoles from each tank: 1) were euthanized and their gut bacterial community was characterized (n = 1 tadpole per tank), 2) remained in their respective tanks after the pond water was changed to remove residual chemicals from the water treatment (n = ≤ 3 tadpoles per tank), or 3) were used to quantify their corticosterone levels in response to water treatment and then exposed to Bd or a solvent control; four tadpoles from each original tank were either exposed to Bd (n = 2) or the solvent control (n = 2) in new tanks. cOn day 27, Bd load was quantified from the skin of tadpoles that were exposed to Bd or the solvent control. dTadpoles that remained in their respective tanks, after the experimental water treatment of atrazine and/or metyrapone, were allowed to metamorphose, which occurred, on average, on day 50. eOn day 84, post-metamorphic (adult) frogs were exposed to Bd or the solvent control and then fBd was quantified on approximately day 100 from the skin of adults (n = ≤ 2 adults per treatment per tank). gOn day 119, adult frogs were euthanized and their gut bacterial community was characterized. Photos by Mark Yokoyama.