We have established ex situ assurance colonies of two endangered Panamanian harlequin frogs, Atelopus certus and Atelopus glyphus, but observed that males fought with each other when housed as a group. Housing frogs individually eliminated this problem, but created space constraints. To evaluate the potential stress effects from aggressive interactions when grouping frogs, we housed male frogs in replicated groups of one, two, and eight. We measured aggressive behavioral interactions and fecal glucocorticoid metabolite (GC) concentrations as indicators of stress in each tank. In both small and large groups, frogs initially interacted aggressively, but aggressive interactions and fecal GCs declined significantly after the first 2 weeks of being housed together, reaching the lowest levels by week 4. We conclude that aggressive interactions in same-sex groups of captive Atelopus may initially cause stress, but the frogs become habituated within a few weeks and they can safely be housed in same-sex groups for longer periods of time.
Citation: Cikanek SJ, Nockold S, Brown JL, Carpenter JW, Estrada A, Guerrel J, et al. (2014) Evaluating Group Housing Strategies for the Ex-Situ Conservation of Harlequin Frogs (Atelopus spp.) Using Behavioral and Physiological Indicators. PLoS ONE 9(2): e90218. https://doi.org/10.1371/journal.pone.0090218
Editor: Claude Wicker-Thomas, CNRS, France
Received: November 8, 2013; Accepted: January 27, 2014; Published: February 25, 2014
This is an open-access article, free of all copyright, and may be freely reproduced, distributed, transmitted, modified, built upon, or otherwise used by anyone for any lawful purpose. The work is made available under the Creative Commons CC0 public domain dedication.
Funding: The authors conducted this research under the auspices of the Panama Amphibian Rescue and Conservation Project, a partnership between Africam Safari, the Cheyenne Mountain Zoo, Defenders of Wildlife, the Houston Zoo, the Smithsonian Conservation Biology Institute, the Smithsonian Tropical Research Institute and Zoo New England. The authors would like to thank the US Fish and Wildlife Service program Wildlife Without Borders, USAID, the Shared Earth Foundation and the Anele Kolohe Foundation for financial support of aspects of this program that made this work possible. The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Competing interests: The authors have declared that no competing interests exist.
Amphibian biodiversity is being lost at an unprecedented rate  prompting the creation of ex-situ assurance colonies of endangered species as part of a global ‘Amphibian Ark’ effort coordinated through the IUCN . Atelopus species are a high priority for rescue and assurance populations because of their susceptibility to the invasive fungal pathogen, Batrachochytrium dendrobatidis (Bd), which has devastated naïve upland amphibian communities throughout Panama , . The Panama Amphibian Rescue and Conservation Project was created in response to these Bd-related declines and consists of two ex-situ facilities in Panama that house populations of amphibians; the El Valle Amphibian Conservation Center (EVACC) and the Smithsonian Tropical Research Institute's Gamboa Amphibian Research Center (Gamboa ARC). Collectively, these facilities house five of the six Panamanian Atelopus species: A. zeteki Dunn, 1933; A. varius (Lichtenstein & Martens, 1856); A. limosus Ibáñez, Jaramillo & Solís, 1995; A. certus Barbour, 1923; and A. glyphus Dunn, 1931. The sixth known harlequin frog species, A. chiriquiensis Shreve, 1936, has not been observed since 1996 and may be extinct .
The Panama Amphibian Rescue Project aims to create assurance colonies of 20 endangered amphibian species and to grow the captive population of each species to a minimum effective population size of 500 individuals , . However, space is a major limiting factor for ex situ programs, and housing frogs in groups would greatly expand our capacity to meet our population management goals. The AZA species survival plan for A. zeteki manages about 2,000 captive Atelopus and frogs are regularly housed in same-sex groups to limit the extended periods of amplexus observed in opposite sex groups (K. Murphy, pers comm). Many of these frogs have been raised in captivity in group-housing situations, and therefore acclimated to group conditions, but it was unclear how readily our wild-caught Atelopus would acclimate to group housing.
To evaluate the levels of stress associated with different housing scenarios for captive Atelopus, we developed behavioral and physiological indicators to quantify stress. Types of Atelopus calls include advertisement, release, territorial, and courtship with the most common being advertisement . Atelopus males also use visual signals, such as semaphore foot-raising, to signal antagonistic behavior , and their territorial behavior has been well studied , , allowing us to compile an ethogram to observe and document aggressive interactions as a behavioral indicator of stress.
Glucocorticoids are a group of steroid hormones that can be used as indicators to evaluate stress, health status, and disease in many species including amphibians , . Glucocorticoid release is the last step of a hormonal cascade that begins in the brain to help an animal react to a stressor , . An animal's internal response to stress involves the activation of the hypothalamic-pituitary-adrenal axis (HPA), and the release of cortisol or corticosterone from the adrenal cortex . These GCs can be measured in urine, feces, plasma, and blood . Blood analyses are the most common, but not always the most practical because of the potential stress of sample collection that would be too invasive to employ on small-bodied, endangered Atelopus, e.g. , , . Methods to evaluate corticosterone in amphibian urine have been developed, validated and tested on several species , , , but handling and manipulating individuals to collect the urine sample is still somewhat invasive, especially with smaller, more delicate frogs. By contrast, fecal pellets are readily collected from captive frogs without disturbance, so we adapted and validated existing fecal GC tests as a non-invasive approach to evaluate physiological stress responses in frogs. The goal of this study was to use behavioral and physiological indicators to determine if wild-caught A. certus and A. glyphus could be maintained in same-sex groups without compromising animal welfare.
Facilities to house wild-caught amphibians from Central America were established in Gamboa, Panama. Collections of from the Darien region were made with permission from the Autoridad Nacional del Ambiente (ANAM) permits SE/A-130-10 and SE/A-42-11. The Animal Care and Use Committee of the Smithsonian National Zoological Park approved the project(#09–31). A total of 44 A. certus and 22 A. glyphus were housed individually in small plastic cages measuring 28×19×16.5 cm for at least 1 year before the start of this 5-week study. Cages were misted daily and enriched with native plant leaves (Philodendron spp.) and damp brown paper towels. Tanks were kept on metal racks with fluorescent overhead lighting for 12 hours per day and cleaned twice per week. At the start of the experiment, frogs were removed from the plastic cages and placed in large, numbered glass tanks (size 25×53×38 cm) with automated misting systems lightly spraying the tank interiors for 5 minutes every 2 hours. Cages had false bottoms installed (plastic egg crate covered in 0.5 mm screen mesh), keeping frogs (and fecal pellets) out of contact with any dirty water that may have pooled on the tank bottom. Ultraviolet-emitting lights supplemented the 12-hour overhead fluorescent lights for eight 45-minute intervals per day. Each tank was furnished with two potted plants (Philodendron spp.), rocks and a water basin. Frogs were randomly assigned to one of three treatments consisting of identical tanks housing one, two, or eight male Atelopus frogs, respectively. Each treatment was replicated 6 times in a completely randomized design. A. glyphus males (mean Snout Vent Length (SVL) = 37 mm SD +/−1.8 mm, 3.76 g SD +/−0.53 g) were used in 2 full replicates, and A. certus males (mean SVL = 32.3 mm SD +/−1.6 mm, 2.65 g SD +/−0.39 g) were used for the remaining 4 replicates. Black, opaque dividers were placed between tanks to limit visual cues from neighbors. Frogs were fed ad libitum with small crickets (Acheta domesticus) or fruit flies (Drosophila melanogaster and D. hydei) dusted with calcium or vitamin supplements 4 times per week. Frogs were weighed and measured (SVL) at the start and end of the experiment. We examined overall weight loss or gain as a measure of body condition, expressed as the relative change in mass as a percentage of the starting weight. We created cage cards using photographs of the unique pattern of dark spots clearly visible on their white ventral side to distinguish between individuals.
A range of territorial and aggressive behaviors were recorded to assess the degree of conflict associated with each group size and defined using an ethogram (Figure 1). Aggressive interactions included fighting, mounting, release-call, stalking, and waving. A single observer (SN) tallied behavior in each tank for 5 minutes twice a day, in the morning between 0700–0830 hr and in the afternoon between 1400–1530 hr. The order of sampling was randomized to prevent any sequential bias due to time of day. All observations in a single week were summed and divided by the number of frogs in each tank to obtain a total number of aggressive interactions observed per frog per week.
Fight: Combat involving mouth or front limbs, often flipping of opponent; Mount: >50% of initiators body covers the victim for >5 seconds; Release call: High pitched, weak, peep like call; maximum tally of one per individual; Physical contact: Any remaining forms of physical contact; Stalk: One individual actively follows/chases another for >5 seconds; Wave: Circular movements in front limbs.
Fecal material was removed manually and tanks were not changed for the duration of the experiment. Each week a single frog produces 5–9 fecal pellets with a mean weight of 0.038 g SD+/−0.026 g. Fecal pellets were stored at −20°C until extraction and analysis of GC metabolite concentrations. Collection began 1 week prior to moving frogs to the glass cages (week 0) to establish baseline GC concentrations. Every solid fecal sample was collected within 12 hours of being voided and all weekly samples from each enclosure were frozen together in 1.5 mL polypropylene tubes until processing. Samples from each cage were pooled by week to obtain a sufficient weight of fecal material for extraction.
Fecal glucocorticoid extraction and analysis
A fecal GC extraction method similar to Brown et al. ,  was used for frog feces. Four solvent:water (v:v) ratios were tested to determine the best recovery: 90% ethanol:dH2O, 80% ethanol:dH2O, 90% methanol:dH2O and 80% methanol:dH2O. The subsequent extracts were serially diluted, analyzed on the cortisol EIA (described below), and compared to the standard curve for parallelism (90% ethanol: r2 = 0.988, F(1,4) = 316.64, p<0.01; 80% ethanol: r2 = 0.980, F(1,4) = 397.92, p<0.01, 90% methanol: r2 = 0.995, F(1,5) = 1093.27, p<0.01 and 80% methanol: r2 = 0.995, F(1,4) = 758.56, p<0.01). For each method, the linear portion of the slope of the curve was similar to the standard curve (standards: −11.74; 90% ethanol: −11.84; 80% ethanol: −11.78; 90% methanol: −10.98 and 80% methanol: −12.16). Although all solvent ratios resulted in high steroid recovery, based on the maximum percent binding (%B) of a neat sample, 90% methanol:10% dH2O was the optimal extraction method (90% ethanol, 41.36%B; 80% ethanol, 38.95%B; 90% methanol, 31.59%B; 80% methanol, 37.04%B). Thus, for this study, wet samples (∼0.05 g) were weighed and placed into 16×125 mm borosilicate tubes. Five mL of 90% methanol:10% dH2O was added to each sample, tubes were capped and then vortexed for 10 seconds. Samples were shaken on a large capacity mixer for 30 minutes (Glas-Col, Terre Haute, Indiana, speed 55, pulse rate 1/second) followed by centrifugation at 2500×g for 20 minutes. The supernatant was recovered, and 5 mL 90% methanol:10% dH2O was again added to each tube. The pellets were re-suspended and the samples were shaken on a large capacity mixer (30 seconds, speed 55, pulse rate 1/second) and centrifuged for 20 minutes. The supernatants were combined, evaporated to dryness under directed air, then reconstituted in 1 mL 100% methanol and placed in an ultrasonic cleaner water bath (Cole Parmer Instrument Company, Vernon Hills, Illinois) for 10 minutes and dried down. Fecal extracts were reconstituted in 1 mL preservative-free buffer (0.2 M NaH2PO4, 0.2 M Na2HPO4, 0.15 M NaCl; pH 7.0), sonicated for 15 minutes, transferred to polypropylene tubes and stored at −20°C until analysis. One hundred µL of 3H-cortisol (∼10,000 cpm/100 µL) was added to monitor extraction efficiency of each sample, which was determined to be 90±0.003% (mean ± SEM) based on recovery of radioactivity after extraction.
Two assays, a cortisol enzyme immunoassay (EIA; C. J. Munro, University of California, Davis, California) and a corticosterone radioimmunoassay (RIA; MP Biomedicals, Santa Ana, California), both of which have broad crossreactivity with fecal GC metabolites in numerous species ,  were evaluated for use with Panamanian golden frog (A. zeteki) feces. Both the corticosterone RIA and cortisol EIA demonstrated parallelism between serial fecal extract dilutions and the respective standard curve. Low matrix interference was indicated in the corticosterone RIA as a result of 88% recovery of known standard concentrations when diluted with equal parts fecal extract pool. For the cortisol EIA, the average recovery was 91%. To compare longitudinal patterns, samples from 11 frogs were analyzed in both assays and the correlation between the two was calculated. The median correlation between the assays for individual fecal GC profiles was high at r = 0.92 (range: 0.57–0.98). Biological validity was shown by a frog that demonstrated a marked increase in GC concentrations within 4 days after ACTH injection (0.2 IU, IM) for both EIA (pre, 13.8 ng/g; post, 66.4 ng/g) and RIA (pre, 2.9 ng/g; post, 15.7 ng/g); the two profiles were correlated (r = 0.93; p<0.001) (Figure 2). Thus, both assays were able to detect similar patterns of hormone excretion; however, the cortisol assay detected higher overall concentrations of metabolites (∼5-fold higher) and so was used in this study.
The single-antibody cortisol EIA was based on the methodology of Munro and Lasley  and used a polyclonal antiserum (R4866) and horseradish peroxidase ligand (lot 051229, SCBI, Front Royal, Virginia). The cross-reactivities for R4866 are: cortisol 100.0%, prednisolone 9.9%, prednisone 6.3%, cortisone 5.0%; all other compounds cross-react with the antibody <1.0% . The standard curve range for the assay was 0.78–20.00 ng/mL. Antiserum was diluted with coating buffer (0.015 M Na2CO3, 0.035 M NaHCO3, pH 9.6) and adsorbed to NUNC Maxi-sorp flat-bottomed, 96-well microtiter plates overnight at 4°C. The plate was washed 5 times (0.05% Tween 20 in 0.15 M NaCl solution), then 50 µL of standards, internal controls and samples were loaded onto the plate in duplicate, followed by the addition of 50 µL diluted horseradish peroxidase solution. Assays were incubated at room temperature for 1 hour, washed 5 times and 100 µL of 2,2′-azinobis [3-ethylbenzothiazoline-6-sulfonic acid]-diammonium salt [ABTS] solution (0.04 M ABTS, 0.5 M H2O2 in 0.05 M citric acid buffer) added to every well. Absorbance was read on a spectrophotometer (MRX, Dynex Technologies, Chantilly, VA, with a 405 nm filter 405 and reference filter of 490 nm) until the optical density (OD) of the 0.00 ng/mL standard reached ∼1.0 (range: 0.9–1.1; desired OD reached within 20–30 min). Steroid concentrations were divided by the amount extracted and reported as ng/g feces. Samples weighing <0.01 g were excluded from the data set because low weight samples consistently exhibited higher values compared to heavier samples . The inter-assay variation on two internal controls (high and low GC concentration) were 7.3 and 8.0% CV, respectively (n = 16). Intra-assay variation between sample duplicates was <10% CV.
High performance liquid chromatography
High performance liquid chromatography (HPLC; Varian ProStar; Varian Analytical Instruments, Lexington, Massachusetts) was used to characterize the numbers and proportions of immunoactive hormone metabolites excreted in Atelopus feces. Three aliquots of pooled fecal samples were extracted as described above, omitting the 3H tracer. The methanol extracts were pooled, dried down under directed air, resuspended in 500 µL PBS (0.03 M Na2HPO4, 0.02 M NaH2PO4, 0.15 M NaCl, 0.002 M NaN3, pH: 5.0), filtered through a C18 Spice cartridge and evaporated to dryness. For chromatographic markers, approximately 14,000 cpm/mL of 3H-cortisol and 3H-corticosterone were each added to the extract. The extract was dried down then reconstituted in 300 µL methanol (HPLC Grade Methanol, Fisher Scientific, Pittsburgh, Pennysylvania) and sonicated for 15 minutes. Then, 50 µL of extract was loaded onto a reverse-phase C18 HPLC column (Agilent Technologies, Santa Clara, California) with a 20–80% linear gradient of HPLC Grade methanol:water over 80 minutes (1 mL/minute. flow rate, 1 mL fractions). A 50 µL aliquot of each fraction was analyzed for radioactivty using a multi-purpose β-radiation scintillation counter (LS 6500, Beckman Coulter, Brea, California). The remaining volume was dried down, reconstituted in 200 µL preservative-free phosphate buffer and analyzed in singlet in the cortisol EIA and corticosterone RIA.
Data were analyzed using SYSTAT 11 software. We performed a repeated measures ANOVA using GC values (ng/g) or feces extracted from pooled weekly fecal samples collected in each tank as the repeated measure, and group size (two frogs per tank vs. eight frogs per tank) was our experimental factor. For the group size of n = 1, one week's worth of fecal pellets was sometimes not enough material to perform an extraction, resulting in too many missing values to be incorporated into the statistical analysis. For the behavioral analysis, we performed repeated measures ANOVA using total number of aggressive interactions observed per frog per week as the repeated measure and group size (two frogs per tank vs eight frogs per tank) as our experimental factor.
High performance liquid chromatography
Based on HPLC analysis, 3H-cortisol eluted at fractions 39–41 and peaked at fraction 40, while peak 3H-corticosterone eluted at fraction 45 (range: 44–46). Immunoactivity of fractions analyzed on the cortisol EIA indicated the presence of native cortisol with a peak at fraction 39 (15% of the total immunoactivity) and a smaller amount of immunoreactivity at fractions 44–45 (11%). Additional immunoreactivity was observed at fraction 13 (6%), and there were peaks of uncharacterized less polar metabolites at fractions 54, 59, 66, 75, and 79 (68% of total immunoactivity). Concentration of GC immunoactivity of HPLC-separated fractions in the corticosterone RIA was only about a tenth that of the cortisol EIA, with small peaks at 37-39 (3%) and 44–48 (11%), and also several less polar peaks of similar levels of immunoreactivity at fractions 50, 54, 59, 63, 65, 76, and 79 (86%).
The most common behavior observed was physical contact, which accounted for 28% of all aggressive interactions included in the ethogram, but for the purposes of this analysis, all aggressive interactions were pooled because no single behavioral response was recorded in high enough frequency to compare behavior types. When we placed groups of both two and eight Atelopus together, aggressive interactions were high at first, but declined significantly in subsequent weeks to a mean of almost zero aggressive interactions observed per frog per week (Figure 3B, Table 1B). There was no significant difference in relative number of aggressive interactions per frog, between groups of 8 and 2 frogs.
Frogs housed singly (mean = 44.2 ng cortisol/g±7.4 SEM) could not be included in this analysis because of too many missing values. Aggressive interactions changed significantly over time (p<0.001***), but there were no significant differences between group sizes.
Similarly, there was a significant increase in fecal GC levels in groups of both two and eight frogs per tank when they were placed together for the first time. Fecal GC concentrations in groups of two and eight individuals rose initially and then declined to their lowest concentrations by week 4 (Figure 3A, Table 1A) when mean fecal glucocorticoid levels approximated the mean glucocorticoid levels of individually housed frogs 44.2±7.4 ng/g. Interestingly, the cortisol levels by the end of the experiment were both lower than the baseline (week = 0) levels obtained when they were being housed individually in small plastic cages. Overall body condition measurements had a high degree of variability, but on average frogs lost 2.6% of their body mass over the 5 weeks SD +/−7.1%. There were no statistically significant differences in changes in body condition between frogs in the different group sizes (Kruskall-Wallace p 0.454).
Fecal glucocorticoid extraction methods
In comparative analyses, a cortisol EIA and corticosterone RIA were both capable of quantifying GC metabolites in Atelopus fecal extracts, and results were highly correlated. The cortisol antibody reacted with metabolites that co-eluted with both tritiated cortisol and corticosterone tracers, and also a number of less polar metabolites. The corticosterone RIA appeared to detect a small amount of native corticosterone, but also significant amounts of less polar metabolites not unlike that observed for the EIA, although at much lower levels. We decided to employ the cortisol EIA because it detected more immunoreactive mass, it is more portable for possible field studies, and does not rely on the use of radioactive tracers.
Behavioral and physiological responses to grouping
We demonstrated that wild-caught male Atelopus do interact aggressively when housed in both small and large groups, but over a relatively short period of time these frogs become accustomed to each other and reduce the frequency of their aggressive interactions. A similar pattern was observed in fecal GC concentrations, indicating that these aggressive interactions are likely associated with a physiological stress response. Interestingly, the mean baseline GC values pre-grouping were higher (60 ng/g) than might have been expected based on the mean GC values observed at the conclusion of the experiment (40 ng/g; Figure 3A). This may be connected to the fact that, prior to the group housing, the smaller holding cages were completely changed twice per week, involving frequent handling of the frog that may have slightly elevated GCs. Once the frogs were transferred to their larger glass cages with automated misting and draining systems we did not need to handle the frogs at all for the duration of the experiment. Many other studies have examined GC levels in amphibians; e.g., , , , , but this is the first time that fecal GCs have been used to evaluate stress in frogs. Our findings are similar to observations by others that group housing of cane toads led to increased urinary corticosterone concentrations that declined once they were moved to individual housing . Measurements of GCs using other methods such urine sampling or buccal swabs can potentially give accurate, short-term measurements e.g. . However, the frogs in this study were not used to handling, so invasive procedures like blood and buccal sample collection would have in themselves induced stress. These approaches would have permitted more fine-scale measurements of acute stress responses, but this was not our objective. Urine is an effective noninvasive approach, but housing conditions of the frogs in our study did not permit reliable sample collection. We also could not partition stress by individual frogs to see if some individuals were experiencing more or less stress than others. But the one major advantage to feces is that it represents a pooled sample over time, so acute fluctuations among and between individuals are dampened. Thus, we conclude that fecal steroid monitoring provides a minimally invasive option to researchers that can be applied, as we have demonstrated here, to evaluate and compare husbandry practices, and how they impact frog welfare over time, as efforts to build global amphibian arks for endangered amphibians continue to grow .
Our results are significant from a conservation perspective because they justify housing frogs in groups. Given that space is a major limiting factor in ex-situ conservation programs, it will greatly increase the number of frogs that can be held in captivity and managed for amphibian conservation and reintroduction efforts. We did not detect a statistically significant effect of group size; this may have been due to low statistical power from having just six replicates. Future studies that increase the number of replicates and treatment groups may shed light on optimal housing densities. It is important to note, however, that housing frogs in groups may have other consequences not addressed in this study. For example, group housing may lead to changes in body condition if smaller or non-dominant animals do not compete as well for food , but this was not observed in this experiment. Group housing may lead to increased buildup of gut parasite loads  or increased aggressive interactions during the breeding season . Any of these could have an impact on the long-term health of an individual if not carefully managed and monitored by animal care staff, and should be considered carefully before making management changes.
Conceived and designed the experiments: SJC SN AE JG RI BG. Performed the experiments: SN SJC KH JG AE. Analyzed the data: SJC JLB JWC BG. Contributed reagents/materials/analysis tools: KH SBP JLB. Wrote the paper: SJC JLB BG JWC.
- 1. Stuart SN, Chanson JS, Cox NA, Young BE, Rodrigues ASL, et al. (2004) Status and Trends of Amphibian Declines and Extinctions Worldwide. Science 306: 1783–1786.
- 2. Zippel K, Johnson K, Gagliardo R, Gibson R, McFadden M, et al. (2011) The Amphibian Ark: a global community for ex situ conservation of amphibians. Herpetological Conservation and Biology 6: 340–352.
- 3. La Marca E, Lips KR, Lotters S, Puschendorf R, Ibáñez R, et al. (2005) Catastrophic population declines and extinctions in neotropical Harlequin frogs (Bufonidae: Atelopus) Biotropica. 37: 190–201.
- 4. Crawford AJ, Lips KR, Bermingham E (2010) Epidemic disease decimates amphibian abundance, species diversity, and evolutionary history in the highlands of central Panama. Proceedings of the National Academy of Sciences:
- 5. Lips K, Ibáñez R, Bolaños F, Chaves G, Solís F, et al. (2008) Atelopus chiriquiensis. IUCN Red List of Threatened Species Version 20102 wwwiucnredlistorg Downloaded on 01 August 2010.
- 6. Schad K (2008) Amphibian Population Management Guidelines. Amphibian Ark Amphibian Population Management Workshop December 10–11, 2007 San Diego: Amphibian Ark, http://www.amphibianark.org/pdf/Aark material/AArk Amphibian Population Management Guidelines.pdf. Accessed Feb 13, 2014.
- 7. Frankham R, Briscoe D, Ballou J (2002) Introduction to conservation genetics: Cambridge Univ Press.
- 8. Jaslow AP (1979) Vocalization and aggression in Atelopus chiriquiensis (Amphibia, Anura, Bufonidae). Journal of Herpetology 13: 141–145.
- 9. Lindquist ED, Hetherington TE (1996) Field Studies on Visual and Acoustic Signaling in the “Earless” Panamanian Golden Frog, Atelopus zeteki. Journal of Herpetology 30: 347.
- 10. Cocroft RB, McDiarmid RW, Jaslow AP, Ruiz-Carranza PM (1990) Vocalizations of eight species of Atelopus (Anura: Bufonidae) with comments on communication in the genus. Copeia: 631–643.
- 11. Crump ML (1986) Homing and Site Fidelity in a Neotropical Frog, Atelopus varius (Bufonidae). Copeia 1986: 438–444.
- 12. Goymann W, Wingfield JC (2004) Allostatic load, social status and stress hormones: the costs of social status matter. Animal Behaviour 67: 591–602.
- 13. Narayan EJ (2013) Non-invasive reproductive and stress endocrinology in amphibian conservation physiology. Conservation Physiology 1: 1–16.
- 14. Romero LM (2004) Physiological stress in ecology: lessons from biomedical research. Trends in Ecology & Evolution 19: 249–255.
- 15. Sapolsky RM, Romero LM, Munck AU (2000) How do glucocorticoids influence stress responses? Integrating permissive, suppressive, stimulatory, and preparative actions. Endocrine reviews 21: 55–89.
- 16. Cockrem JF, Barrett DP, Candy EJ, Potter MA (2009) Corticosterone responses in birds: Individual variation and repeatability in Adelie penguins (Pygoscelis adeliae) and other species, and the use of power analysis to determine sample sizes. General and comparative endocrinology 163: 158–168.
- 17. Sheriff MJ, Dantzer B, Delehanty B, Palme R, Boonstra R (2011) Measuring stress in wildlife: techniques for quantifying glucocorticoids. Oecologia 166: 869–887.
- 18. Belden L, Moore I, Mason R, Wingfield J, Blaustein A (2003) Survival, the hormonal stress response and UV avoidance in Cascades Frog tadpoles (Rana cascadae) exposed to UVB radiation. Functional Ecology 17: 409–416.
- 19. Gendron AD, Bishop CA, Fortin R, Hontela A (1997) In vivo testing of the functional integrity of the corticosterone-producing axis in mudpuppy (amphibia) exposed to chlorinated hydrocarbons in the wild. Environmental Toxicology and Chemistry 16: 1694–1706.
- 20. Narayan EJ, Molinia FC, Kindermann C, Cockrem JF, Hero J-M (2011) Urinary corticosterone responses to capture and toe-clipping in the cane toad (Rhinella marina) indicate that toe-clipping is a stressor for amphibians. General and comparative endocrinology 174: 238–245.
- 21. Narayan EJ, Cockrem JF, Hero J-M (2013) Sight of a Predator Induces a Corticosterone Stress Response and Generates Fear in an Amphibian. PLoS one 8: e73564.
- 22. Narayan EJ, Cockrem JF, Hero J-M (2011) Urinary corticosterone metabolite responses to capture and captivity in the cane toad Rhinella marina. General and comparative endocrinology 173: 371–377.
- 23. Graham LH, Brown JL (1996) Cortisol metabolism in the domestic cat and implications for non-invasive monitoring of adrenocortical function in endangered felids. Zoo Biology 15: 71–82.
- 24. Brown JL, Wasser SK, Wildt DE, Graham LH (1994) Comparative aspects of steroid hormone metabolism and ovarian activity in felids, measured noninvasively in feces. Biology of reproduction 51: 776–786.
- 25. Wasser SK, Hunt KE, Brown JL, Cooper K, Crockett CM, et al. (2000) A generalized fecal glucocorticoid assay for use in a diverse array of nondomestic mammalian and avian species. General and comparative endocrinology 120: 260–275.
- 26. Young K, Walker S, Lanthier C, Waddell W, Monfort SL, et al. (2004) Noninvasive monitoring of adrenocortical activity in carnivores by fecal glucocorticoid analyses. General and comparative endocrinology 137: 148–165.
- 27. Munro C, Lasley B (1988) Non-radiometric assays: technology and application in polypeptide and steroid hormone detection. Non-radiometric methods for immunoassay of steroid hormones. New York: Allan Liss Corporation. pp. 289–329.
- 28. Millspaugh JJ, Washburn BE (2004) Use of fecal glucocorticoid metabolite measures in conservation biology research: considerations for application and interpretation. General and comparative endocrinology 138: 189–199.
- 29. Haislip NA, Hoverman J, Miller DL, Gray MJ (2012) Natural stressors and disease risk: does the threat of predation increase amphibian susceptibility to ranavirus? Canadian Journal of Zoology 90: 893–902.