ArticlePDF Available

Batrachochytrium dendrobatidis infection and treatment in the salamanders Ambystoma andersoni, A. dumerilii and A. mexicanum

Authors:
  • Association of Zoo and Exotic Veterinary Nurses
  • Zoo Thoiry

Abstract

In order to better understand the impacts of treatment of infection with Batrachochytrium dendrobatidis (Bd) and Batrachochytrium salamandrivorans (Bsal) it is important to document host species, the effect of infection and response to treatment protocols. Here we report asymptomatic Bd infection detected through duplex qPCR screening of three Mexican ambystomatid salamanders; Ambystoma andersoni, Ambystoma dumerilii and Ambystoma mexicanum at three zoo collections, and A. andersoni and A. mexicanum in a private collection. Bsal was tested for but not detected. We also report the effectiveness and side effects of five treatment protocols in these species. Using the antifungal agent itraconazole, A. dumerilii were cleared of infection without side-effects using the granulated preparation (Sporanox). Morbidity and mortality occurred when A. dumerilii and A. andersoni were treated using a liquid oral preparation of the itraconazole (Itrafungol); infection was successfully cleared in surviving specimens of the latter species. Ambystoma mexicanum was successfully cleared without any side-effects using Itrafungol. Mortality and morbidity were likely caused by toxic effects of some component on the liquid preparation of itraconazole, but aspects of water quality and husbandry cannot be ruled out.
87
Batrachochytrium dendrobadis
Ambystoma andersoni, A. dumerilii
A. mexicanum
Christopher J. Michaels1, Mahew Rendle1, Cathy Gibault2, Javier Lopez3, Gerardo Garcia3,
Mahew W. Perkins4, Suzea Cameron5 & Benjamin Tapley1
1 Zoological Society of London (ZSL) London Zoo, Regent's Park, London, NW1 4RY, UK
2 Parc de Thoiry, Rue du Pavillon de Montreuil, 78770, Thoiry, France
3 Chester Zoo, Moston Rd, Upton-by-Chester, Upton, Chester, CH2 1EU, UK
4 ZSL Instute of Zoology, Moston Rd, Upton-by-Chester, Upton, Chester, CH2 1EU, UK
5Birch Heath Veterinary Clinic, Birch Heath Road, Tarporley CW6 9UU, UK
Herpetological Journal SHORT NOTE
Correspondence: Christopher Michaels (
christopher.michaels@zsl.org
)
Volume 28 (April 2018), 87-92
Published by the Brish
Herpetological Society
Batrachochytrium dendrobatidis (Bd; Longcore et
al., 1999) is a major fungal pathogen known to
infect all orders of amphibian (Gower et al., 2013)
and is a driver of population declines (Bosch et al.,
2001; Lips et al., 2006; Briggs et al., 2010; Scheele
et al., 2017). The recently described congener
B. salamandrivorans (Bsal; Martel et al., 2013) also
causes disease and its spread is a cause for major concern
(Martel et al., 2014; Richgels et al., 2016; Spitzen-van
der Sluijs 2016; Laking et al., 2017). Bsal is thought to
be less cosmopolitan than the globally distributed Bd
(Fisher et al., 2009; Sabino-Pinto et al., 2016); however,
surveys of captive and free-living populations are far
from comprehensive.
In capvity, a variety of chemical treatments as well
as heat therapy (27-37 ˚C) have been used to treat the
chytrid infecons caused by both agents (e.g. Berger et
al., 2004; Bowerman et al., 2010; Chaield and Richards-
Zawacki 2011; Martel et al., 2011; Woodhams et al.,
2003, 2012; Brannelly et al., 2012; Blooi et al., 2015a;
b). However, urodelan amphibians tend to exhibit low
tolerances to elevated temperatures (e.g. Liu et al.,
2006; Bury, 2008), which oen precludes heat treatment
as a viable method to clear Bd infecon. It is therefore
imperave that the ecacy of other treatment opons
is tested.
Successful therapy using itraconazole has been
documented in numerous amphibian species from all
three orders (Forzan et al., 2008; Tamukai et al., 2011;
Brannelly et al., 2012; Rendle et al., 2015), but dierent
species respond differently to the drug. Itraconazole
toxicosis has been reported in some amphibian species
treated at ‘routine’ doses of the drug (Garner et al.,
2009; Woodhams et al., 2012). It has therefore been
recommended to record the effects of Bd on host
animals and to develop and test protocols for treang
this widespread pathogen in a variety of species of
amphibian (Woodhams et al., 2012).
We present data following Bd diagnosis and
subsequent treatments of 40 Ambystoma dumerilii,
26 A. mexicanum and 10 A. andersoni in capvity (see
Supplementary Materials for details). Animals were
maintained according to the protocols outlined in Table 1
at the Zoological Society of London (ZSL), Chester Zoo (CZ),
Parc de Thoiry (PT) and a private breeder in the UK (PB).
Salamanders were sampled inially and post treatment
(see Table 1) for Bd/Bsal screening by swabbing dorsum,
In order to beer understand the impacts and treatment
of infecon with Batrachochytrium dendrobadis (Bd) and
Batrachochytrium salamandrivorans (Bsal) it is important to
document host species, the eect of infecon and response
to treatment protocols. Here we report asymptomatic
Bd infecon detected through duplex qPCR screening of
three Mexican ambystomad salamanders; Ambystoma
andersoni, Ambystoma dumerilii and Ambystoma
mexicanum at three zoo collecons, and A. andersoni and
A. mexicanum in a private collecon. Bsal was tested for
but not detected. We also report the eecveness and side
eects of ve treatment protocols in these species. Using
the anfungal agent itraconazole, A. dumerilii were cleared
of infection without side-effects using the granulated
preparaon (Sporanox). Morbidity and mortality occurred
when A. dumerilii and A. andersoni were treated using
a liquid oral preparaon of the itraconazole (Itrafungol);
infecon was successfully cleared in surviving specimens of
the laer species. Ambystoma mexicanum was successfully
cleared without any side-eects using Itrafungol. Mortality
and morbidity were likely caused by toxic eects of some
component on the liquid preparaon of itraconazole, but
aspects of water quality and husbandry cannot be ruled
out.
Key words: Bd, axolotl, Ambystoma, chytridiomycosis,
itraconazole
88
ventrum, cloaca, lips, tail base and plantar aspect of the
feet using a sterile dry swab (see Table 1 for numbers
of swabs collected and Supplementary Materials for
swabbing methods). Duplex qPCR was used to test for
the presence of Bd and Bsal DNA following protocols
developed by Hya et al. (2007) and Blooi et al. (2013)
(see Supplementary Materials). Itraconazole baths were
used for treatment in all instuons using the protocols
outlined in Table 2 and detailed in Supplementary
Materials. Results of initial and post-treatment qPCR
tesng, including Genomic Equivalent (GE) values, are
presented in Table 1; all species presented with at least
some animals infected with Bd, but Bsal was not detected.
All animals that survived treatment tested negave for
both pathogens aer treatment (Table 2). Idencaon
of the lineage or strain of Bd infecng animals (Retallick
& Miera, 2007) was beyond the scope of this work.
All surviving salamanders in all collecons repeatedly
tested negave for Bd post treatment (see Table 2). At
ZSL and PT, there were no observed adverse side eects
to treatment with Sporanox in A. dumerilii. Water quality
was monitored at ZSL and PT, and remained good (see
Table 1). At CZ, there was 100% mortality of animals
shortly aer exposure to the treatment regimen using
Itrafungol. Water quality was not monitored at CZ. At CZ
on day 7 of treatment with Itrafungol, six A. dumerilii were
found dead. The remaining animals exhibited excessive
mucus production, cloudy eyes, erratic movements
and inappetence. At post mortem examination and
subsequent histopathology, the salamanders were thin
and presented acute dermas (somemes ulcerave
or necrotic) and branchitis. Some specimens showed
hepatocyte vacuolation. Treatment was stopped but
aer two days, the condion of the remaining animals
had connued to worsen and they were euthanased on
welfare grounds. No CZ animals completed the treatment
protocol.
At PB, A. mexicanum showed no clinical adverse
eects of treatment with Itrafungol. In A. andersoni, 50%
mortality was encountered when treated with Itrafungol.
 Ambystoma dumerilii A. mexicanum A. andersoni
    
 P 3 indi-
vidual swabs

 11 indi-
vidual swabs
 2 pooled
swabs, 8 individuals each
2
pooled swabs, eight indi-
viduals each
 5
pooled swabs, 3 individuals
each; 1 individual swab
13
individual swab
 N/A
 1
pooled swab for 4 A.
mexicanum

 1 pooled swab
for 4 A. mexicanum
 1
pooled swab for 2 A.
andersoni

 1 pooled swab
for 2 A. andersoni


 3/3 +ve,
 6.48,
12.6, 2964.12 GE
 3/3 -ve
 1/2 two pooled swabs
+ve.
 2/2 pooled swabs
-ve.
 6/13 +ve,

31, 41.64, 84.72,
97.44, 114.72,
704.76 GE
 13/13 -ve
 +ve
-ve
 +ve
-ve



3-4 animals held in 100
x 30 x 30 cm aquaria
Aquaria ltered using
air-stream sponge
lters.
5 animals in a 100 x 50
x 60 cm aquarium; 11
animals individually in 40
x 30 x 30 cm plasc boxes.
Large aquarium lter with
internal lter. Small boxes
unltered; 100% water
change performed daily.
4-5 animals held in
400L aquaria.
Large plasc boxes (varying capacity).
No ltraon.
Daily 100% water changes and disinfecon
of enclosures.




 c. 8

+ 0 -
0.03mg/L (with two
brief instances of c.
0.5mg/L)
2
0-0.04mg/L (with one
instance of c. 0.5mg/L
 <10 mg/l
 175-
200mg/L
15-17 ˚C
 6.8 - 7.2
2 0mg/L
 50 - 75 mg/l
 370 micro
Siemens.
 18 ˚C
Water parameters
not recorded.
 7.9.
16-20 ˚C.
 Husbandry and swabbing protocols for Ambystoma salamanders reported in this study
C. Michaels et al.
89
Bd infection and treatment in axolotls
At PB, A. mexicanum showed no clinical adverse eects
of the Itrafungol treatment. In A. andersoni, however,
animals lost vigour during treatment and within one week
of compleon of treatment, ve animals had died (50%
mortality). Animals exhibited shrinking gill branches, loss
of gill laments both of which were noceable in living
and dead animals. Animals also showed reduced feeding
behaviour. Ten days post treatment, surviving animals
were removed from the established aquarium into
which they had been placed and maintained in a 160L
plasc box with 100% daily water changes. Following this
intervenon, mortality stopped and animals recovered
to normal appearance and behaviour. No histological
data are available from these animals.
Bd infecon has not previously been reported from A.
dumerilii or A. andersoni, but has been recorded in other
neotenic Mexican Ambystoma (namely A. altamirani, A.
granulosum, A. mexicanum, A. rivulare, A. ordinarium
and A. velasci; Forzan et al., 2008; Frias-Alvarez et al.,
2008; Galindo-Bustos et al., 2014; Spitzen-van der Sluijs
et al., 2011). Animals of all three species in all four
collecons were apparently able to carry Bd infecon
without clinical disease. This has been reported in other
ambystomad salamanders (Spitzen-van der Sluijs et al.,
2011; Davidson et al., 2003; Padge-Flohr, 2008) and
this may be linked to the producon of skin pepdes
that inhibit the growth of Bd (Sheafor et al., 2008). Our
data suggest that all three species invesgated here may
be able to act as reservoirs of Bd, at least within capve
populaons and, potenally, in nature.
In A. dumerilii, infecon loads, in terms of GE per
sample, were broadly similar overall between Chester
Zoo and ZSL (Table 1), but variaon within species was
substanal. All but one swabbed animal (ZSL; 2964.12
GE) had very low loads. Ambystoma mexicanum in a Bd
posive laboratory colony were reported to have loads
of 0 - 1726.29 GE (Frias Alvarez et al., 2008). Although
the highest infecon load in A. dumerilii is approximately
40% higher than the maximum infecon load reported
in A. mexicanum, no measure of variaon was given by
Frias-Alverez et al. (2008) and so direct comparison with
our data is not possible. The use of pooled swabbing at
Parc de Thoiry for A. dumerilii, and for A. andersoni and
A. mexicanum in the private collecon precluded any
esmaon of infecon intensity and so comparisons with
the literature are not possible.
For unknown reasons, Bd was not detected on some
A. dumerilii individuals within Bd posive groups; this can
probably be regarded as represenng the boom end of
the detected variaon in infecon loads between infected
salamanders. This observaon mirrors circumstances
reported in colonies of A. mexicanum in both laboratory
(Frias Alvarez et al., 2008) and zoo (Galindo-Bustos et
al., 2014) sengs. Labial swabs, alongside samples from
other sites, were collected as some larval ambystomad
salamanders possess keranized jaw sheaths that may
act as infecon foci for Bd (Venesky et al., 2010) as well
as keran elsewhere on the body (Bosch and Marnez-
Solano, 2006), and so it is likely that swabbing was as
ecient as possible for the collecon of chytrid DNA.
Although these results are likely to reect real negaves,
extremely low infecon burdens below the detecon
threshold are also possible.
All animals in this study tested negative for Bsal
infecon, although the animals were maintained within
the opmal temperature range for this fungus (Martel
et al., 2013; Blooi et al., 2015a). Negave results are
important in delineating the overall presence of Bsal
 Ambystoma dumerilii A. mexicanum A. andersoni
    


Itraconazole (Sporanox;
Janssen Pharamceuca N.V.,
Beerse B-2340, Belgium).
Itraconazole (Itrafungol; Elanco,
Division Eli Lilly Canada Inc.,
150 Research Lane, Suite 120,
Guelph, ON, N1G 4T2, Canada)
Itraconazole (Itrafungol)
Therapeuc
itraconazole
concentraon,
duraon and tem-
perature
0.01%. 15 minute baths
daily for eleven days at c.
16 ˚C.
 0.01%. 7 minute
baths daily for seven days.
 0.005%. 15
minute baths daily for seven days
Both versions at c. 18˚C.
0.01%. 5 minute baths daily
for ten days, followed by 10
rest days and then a further
ten days of 5 minute baths.
Treatment course not com-
pleted due to mortality.
Water temperature not
recorded.
0.01% in buered with one
tsp NaHCl/5L tap water to
maintain pH 7.
5 minutes per day, daily
over six days.
16-20 ˚C.
Treatment protocol Animals were moved to
individual c. 1L containers
of itraconazole soluon.
Filtered aquaria were not
sterilised between treat-
ments in order to preserve
biological ltraon.
Animals were to be bathed in 1
litre of soluon in a clear plasc
bag. Aquaria and lters sterilized
with 1:500 F10 disinfectant aer
5 and 10 days of treatment.
Treatment was not completed.
Animals bathed in individual 1L containers. Enclosures
sterilised between treatments.
Mortality 0% 100% (animals either died from
presumed toxicosis or were
euthanased)
A. mexicanum: 0% A. andersoni: 50%
Bd negave post
treatment?
Y Animals did not survive treat-
ment
Y Y
 Protocols for and outcomes of itraconazole treatment in Ambystoma salamanders reported in this study.
90
in capve populaons. These results contribute to the
current belief that Bsal infecon is sll relavely rare in
capve urodelans (Sabino-Pinto et al., 2016).
Our results show that Bd infecon can be eliminated
using the established an-fungal chemical itraconazole
in neotenic A. dumerilii, A. mexicanum and A. andersoni.
Treatment with itraconazole of conrmed Bd infecon in
neotenic Ambystoma has not been previously reported.
Metamorphosed A. grinum were successfully cleared
of Bd infecon using a similar protocol to that described
here (10 minute 0.01% itraconazole (Itrizole oral soluon)
baths every other day for seven treatments; Tamukai et
al., 2011). The variaons employed by Thoiry and the
private keeper demonstrate that Bd infection can be
treated, at least in this case, by using a lower itraconazole
soluon (0.005%) and shorter bath duraon (5 minutes)
than the 0.01% and 10-minute immersion me typically
used for treang Bd infecon (Jones et al., 2012). This is
congruent with trials in the anurans Litoria caerulea and
Anaxyrus baxteri (0.005% itraconazole baths in Sporanox
form; Jones et al., 2012) and indicates that low dosage
and short immersion me may be useful in a wide range
of amphibian taxa, at least with low infecon loads.
Dierent preparaons of itraconazole appear to have
different effects and efficacy in different Ambystoma
species. The granule (Sporanox) preparation of
itraconazole can apparently be used without deleterious
side eects in A. dumerilii (this study) and A. mexicanum
(Forzan et al., 2008), while liquid preparations are
apparently safe for use in A. mexicanum (this study;
Itrafungol) and in A. grinum (Itrizole Oral Soluon 1%,
Janssen Pharmaceucal K.K., Tokyo, Japan; Tamukai et
al., 2011). However, our data suggest that use of the
liquid preparaon (Itrafungol) of itraconazole may be
linked to rapid morbidity and mortality in A. dumerilii
and A. andersoni. As water quality was not measured
in collecons using Itrafungol, and as other aspects of
husbandry including disinfecon of lter media co-varied
with treatment regimen, it is possible that detrimental
eects observed were caused by factors other than the
drug. However, deleterious side-eects have also been
recorded in anuran tadpoles treated with Itrafungol
(Garner et al., 2009). We found no evidence in the
literature suggesng either safe use or toxic eects of
any non-itraconazole ingredient (see Supplementary
Materials) of Itrafungol on amphibians. Although
the acve ingredient is the same in both compounds
(itraconazole), there may also have been interactive
eects between itraconazole and other compounds in
the drug, for example through eects on bioavailability
of the active compound. The Itrafungol solution was
buered at PB, but not at CZ. This may have an eect on its
ecacy against Bd (e.g. pH aects Bd growth; Piotrowski
et al., 2004) and any side-eects on the salamanders
themselves, but this preparaon led to morbidity and
mortality in both collecons. We recommend that the
use of this preparaon should probably be treated with
cauon in ambystomad salamanders.
The deleterious side-eects reported here represent
only impacts on health that can be detected in the short
term. It is possible that other eects on health may be
more subtle or require more longitudinal studies to
detect. Furthermore, the treatment designs used here
were based on previous reports of successful treatments
and do not represent targeted or evidence-based
approaches. The use of data from in vitro exposures of
fungus to candidate treatment regimens could inform
the selecon of the lowest dose and shortest exposures
possible to successfully eliminate the pathogen (e.g.
Martel et al., 2011). Such an approach may avoid negave
side-effects and reduce the chance of unforeseen
negative outcomes of treatment attempts, although
suscepbility of the fungus in vitro does not necessarily
equate to successful therapy in vivo (Berger et al., 2010).
We also demonstrate that Bd infection can be
successfully treated without sterilisaon of biological
filters. This is congruent with Rendle et al. (2015)
and reinforces that a balance can be struck between
eecve therapy and the maintenance of appropriate
environmental parameters. By disinfecting biological
filters between itraconazole treatments, and unless
other methods of dealing with nitrogenous waste (e.g.
chemical ltraon) are employed, the environment in
which animals are kept may rapidly become toxic due to
the accumulaon of waste products. As Bd can, on the
basis of these and other data, be eliminated without the
disinfecon of the environment, biological lters may be
le intact during the treatment of aquac amphibians for
Bd. Bd can survive outside amphibian hosts (Johnson &
Speare, 2003). We were unable to determine if infecve
colonies of Bd survived on the lter media post treatment,
but repeated and long term negave Bd results suggest
that such colonies were either absent or at least unable
to re-infect salamanders.

The authors would like to extend our thanks to keeping
and veterinary sta at ZSL (Iri Gill, Luke Harding, Daniel
Kane, Joe-Smiley Capon-Doyle, Martin Franklin, Nic
Masters, Heather Macintosh, Sophie Sparrow, Mary-
Anne Jones and Jo Korn), at Chester Zoo and at Parc de
Thoiry (Roseline Chambaud, Fanny Grados and Guillaume
Vialaret). We would also like to thank Mark Pickstock,
Debbie Moore and Pinmoore Animal Laboratory Services
for providing us with data for A. mexicanum and A.
andersoni.

Berger, L., Speare, R., Hines, H.B., Marantelli, G., Hya, A.D.,
McDonald, K.R., Skerra, L.F., Olsen, V., Clarke, J.M., Gillespie,
G. & Mahony, M. (2004). Eect of season and temperature on
mortality in amphibians due to chytridiomycosis. Australian
Veterinary Journal 82, 434–439.
Berger, L., Speare, R., Pessier, A., Voyles, J. & Skerratt, L.F.,
(2010). Treatment of chytridiomycosis requires urgent
clinical trials. Diseases of Aquac Organisms 92, 165-174.
Blooi, M., Pasmans, F., Longcore, J.E., Spitzen-van der Sluijs,
A., Vercammen, F. & Martel, A. (2013). Duplex real-me
PCR for rapid simultaneous detecon of Batrachochytrium
dendrobadis and Batrachochytrium salamandrivorans in
C. Michaels et al.
91
amphibian samples. Journal of Clinical Microbiology 51,
4173–4177.
Blooi, M., Martel, A., Haesebrouck, F., Vercammen, F., Bonte, D.
& Pasmans, F. (2015a). Treatment of urodelans based
on temperature dependent infection dynamics of
Batrachochytrium salamandrivorans. Scienc Reports 5,
8037.
Blooi, M., Pasmans, F., Rouaer, L., Haesebrouck, F,. Vercammen,
F. & Martel, A. (2015b). Successful treatment of
Batrachochytrium salamandrivorans infections in
salamanders requires synergy between voriconazole,
polymyxin E and temperature. Scienc Reports 5, 11788.
Bosch, J., Martı́nez-Solano, I. & Garcı́a-Parı́s, M. (2001).
Evidence of a chytrid fungus infection involved in the
decline of the common midwife toad (Alytes obstetricans)
in protected areas of central Spain. Biological Conservaon
206, 331–7.
Bosch, J. & Marnez-Solano, I. (2006). Chytrid fungus infecon
related to unusual mortalies of Salamandra salamandra
and Bufo bufo in the Penalara Natural Park, Spain. Oryx 40,
84–89.
Bowerman, J., Rombough, C., Weinstock, S.R. & Padge-Flohr,
G.E. (2010). Terbinane hydrochloride in ethanol eecvely
clears Batrachochytrium dendrobatidis in amphibians.
Journal of Herpetological Medicine and Surgery 20, 24–28.
Brannelly, L.A., Richards-Zawacki, C.L. & Pessier, A.P. (2012).
Clinical trials with itraconazole as a treatment for chytrid
fungal infections in amphibians. Diseases of Aquatic
Organisms 101, 95–104.
Briggs, C.J., Knapp, R.A. & Vredenburg V.T. (2010). Enzooc and
epizootic dynamics of the chytrid fungal pathogen of
amphibians. Proceedings of the National Academy of
Sciences 107, 9695–9700.
Bury, R.B. (2008). Low thermal tolerances of stream amphibians
in the Pacific north-west, Implications for riparian and
forest management. Applied Herpetology 5, 63–74.
Chatfield, M.W. & Richards-Zawacki, C.L. (2011). Elevated
temperature as a treatment for Batrachochytrium
dendrobadis infecon in capve frogs. Diseases of Aquac
Organisms 94, 235–238.
Davidson, E.W., Parris, M., Collins, J.P., Longcore, J.E, Pessier,
A.P. & Brunner, J. (2003). Pathogenicity and transmission
of chytridiomycosis in tiger salamanders (Ambystoma
grinum). Copeia 2003, 601–7.
Fisher, M.C., Garner, T.W. & Walker, S.F. (2009). Global
emergence of Batrachochytrium dendrobatidis and
amphibian chytridiomycosis in space, time, and host.
Annual Review of Microbiology 63, 291–310.
Forzan, M., Gunn, H. & Sco, P. (2008). Chytridiomycosis in an
aquarium collection of frogs, diagnosis, treatment, and
control. Journal of Zoo and Wildlife Medicine 39, 406–411.
Frías-Alvarez, P., Vredenburg, V.T., Familiar-López, M., Longcore,
J.E., González-Bernal, E., Santos-Barrera, G., Zambrano, L. &
Parra-Olea, G. (2008). Chytridiomycosis survey in wild and
capve Mexican amphibians. EcoHealth 5, 18–26.
Galindo-Bustos, M.A., Hernandez-Jauregui, D.M.B., Cheng, T.,
Vredenburg V. & Parra-Olea, G. (2014). Presence and
prevalence of Batrachochytrium dendrobatidis in
commercial amphibians in Mexico City. Journal of Zoo and
Wildlife Medicine 45, 830–835.
Garner, T.W.J., Garcia, G., Carroll, B. & Fisher, M.C., (2009). Using
itraconazole to clear Batrachochytrium dendrobatidis
infection, and subsequent depigmentation of Alytes
muletensis tadpoles. Diseases of Aquac Organisms 83,
257–260.
Gower, D.J., Doherty-Bone, T., Loader, S.P., Wilkinson, M.,
Kouete, M.T., Tapley, B., Orton, F., Daniel, O.Z., Wynne, F.,
Flach, E. & Müller, H. (2013). Batrachochytrium dendrobadis
infecon and lethal chytridiomycosis in caecilian amphibians
(Gymnophiona). EcoHealth 10,173–83.
Hyatt, A.D., Boyle, D.G., Olsen, V., Boyle, D.B., Berger, L.,
Obendorf, D., Dalton, A., Kriger, K., Heros, M., Hines, H.,
Phillo, R., Campbell, R., Marantelli, G., Gleason, F. & Coiling,
A. (2007). Diagnosc assays and sampling protocols for the
detecon of Batrachochytrium dendrobadis. Diseases of
Aquac Organisms 73, 175–192.
Johnson, M.L., Berger, L., Philips, L. & Speare, R. (2003). Fungicidal
effects of chemical disinfectants, UV light, desiccation
and heat on the amphibian chytrid Batrachochytrium
dendrobadis. Diseases of Aquac Organisms 57, 255–260.
Johnson, M.L. & Speare, R. (2003). Survival of Batrachochytrium
dendrobatidis in water, quarantine and disease control
implicaons. Emerging Infecous Diseases 9, 922–925.
Jones, M.E., Paddock, D., Bender, L., Allen, J.L., Schrenzel, M.D.
& Pessier, A.P. (2012). Treatment of chytridiomycosis with
reduced-dose itraconazole. Diseases of Aquac Organisms
99, 243–249.
Laking, A.E., Ngo, H.N., Pasmans, F., Martel, A. & Nguyen, T.T.
(2017). Batrachochytrium salamandrivorans is
the predominant chytrid fungus in Vietnamese
salamanders. Scienc Reports 7, 44443.
Lips, K.R., Brem, F., Brenes, R., Reeve, J.D., Alford, R.A., Voyles,
J., Carey, C., Livo, L., Pessier, A.P. & Collins, J.P. (2006).
Emerging infecous disease and the loss of biodiversity in
a Neotropical amphibian community. Proceedings of the
Naonal Academy of Sciences 103, 3165–70.
Liu, J., Tan ,Y., Tan, Q., He, X., Zhang, Y. & Liu, M. (2006).
Research on Chinese giant salamander F2 adaptability and
growth advantages. Sichuan Journal of Zoology 25, 387–
390.
Longcore, J.E., Pessier, A.P. & Nichols, D.K. (1999).
Batrachochytrium dendrobadis gen. et sp. nov., a chytrid
pathogenic to amphibians. Mycologia 91, 219–227.
Martel, A., Van Rooij, P., Vercauteren, G, Baert, K., Van
Waeyenberghe, L., Debacker, P., Garner, T.W., Woeltjes,
T., Ducatelle, R., Haesebrouck, F. & Pasmans, F. (2011).
Developing a safe anfungal treatment protocol to eliminate
Batrachochytrium dendrobadis from amphibians. Medical
Mycology 49, 143–149.
Martel, A., Spitzen-van der Sluijs, A., Blooi, M., Bert, W.,
Ducatelle, R., Fisher, M.C., Woeltjes, A., Bosman, W., Chiers,
K., Bossuyt, F. & Pasmans, F. (2013). Batrachochytrium
salamandrivorans sp. nov. causes lethal chytridiomycosis
in amphibians. Proceedings of the Naonal Academy of
Sciences 110, 15325–15329.
Martel, A., Blooi, M., Adriaensen, C., Van Rooij, P., Beukema,
W., Fisher, M.C., Farrer, R.A., Schmidt, B.R, Tobler, U., Goka,
K,. & Lips, K.R. (2014). Recent introduction of a chytrid
fungus endangers Western Palearcc salamanders. Science
346, 630–631.
Padge-Flohr, G.E. (2008). Pathogenicity of Batrachochytrium
dendrobadis in two threatened California amphibians,
Bd infection and treatment in axolotls
92
Rana draytonii and Ambystoma californiense. Herpetol
Conservaon Biology 3,182–91.
Piotrowski, J.S., Annis, S.L. & Longcore, J.E., (2004). Physiology
of Batrachochytrium dendrobadis, a chytrid pathogen of
amphibians. Mycologia 96, 9-15.
Rendle, M.E., Tapley, B., Perkins, M., Bittencourt-Silva, G.,
Gower, D.J. & Wilkinson, M. (2015). Itraconazole treatment
of Batrachochytrium dendrobadis (Bd) infecon in capve
caecilians (Amphibia, Gymnophiona) and the first case
of Bd in a wild neotropical caecilian. Journal of Zoo and
Aquarium Research 3, 137–140.
Retallick, R.W. & Miera, V. (2007). Strain differences in the
amphibian chytrid Batrachochytrium dendrobatidis and
non-permanent, sub-lethal eects of infecon. Diseases of
Aquac Organisms 75,201–207.
Richgels, K.L., Russell, R.E., Adams, M.J., White, C.L & Grant,
E.H.C. (2016). Spaal variaon in risk and consequence of
Batrachochytrium salamandrivorans introducon in the
USA. Royal Society Open Science 3, 150616.
Sabino-Pinto, J., Bletz, M.C., Islam, M.M., Shimizu, N., Bhuju,
S., Geffers, R., Jarek, M., Kurabayashi, A. & Vences, M.
(2016). Composion of the cutaneous bacterial community
in Japanese amphibians, eects of capvity, host species,
and body region. Microbial Ecology 72, 460–469.
Scheele, B.C., Skerra, L.F., Grogan, L.F., Hunter, D.A, Clemann,
N., McFadden, M., Newell, D., Hoskin, C.J., Gillespie,
G.R., Heard, G.W. & Brannelly, L. (2017). After the
epidemic, Ongoing declines, stabilizaons and recoveries
in amphibians afflicted by chytridiomycosis. Biological
Conservaon 206, 37–46.
Sheafor, B., Davidson, E.W., Parr, L. & Rollins-Smith, L. (2008).
Antimicrobial peptide defenses in the salamander,
Ambystoma tigrinum, against emerging amphibian
pathogens. Journal of Wildlife Diseases 44, 226–36.
Spitzen-van der Sluijs, A., Martel, A., Wombwell, E., Van Rooij,
P., Zollinger, R., Woeltjes, T., Rendle, M., Haesebrouck, F. &
Pasmans, F. (2011). Clinically healthy amphibians in capve
collecons and at pet fairs, a reservoir of Batrachochytrium
dendrobadis. Amphibia-replia 32, 419–23.
Spitzen-van der Sluijs, A., Martel, A., Asselberghs, J., Bales,
E.K., Beukema, W., Bletz, M.C., Dalbeck, L., Goverse,
E., Kerres, A., Kinet, T. & Kirst, K. (2016). Expanding
distribuon of lethal amphibian fungus Batrachochytrium
salamandrivorans in Europe. Emerging Infecous Diseases
22, 1286–1288.
Tamukai, K., Une, Y., Tominaga, A., Suzuki, K. & Goka, K. (2011).
Treatment of spontaneous chytridiomycosis in captive
amphibians using itraconazole. The Journal of Veterinary
Medical Science 73, 155–159.
Venesky, M.D., Parris, M.J. & Alg, R. (2010). Pathogenicity of
Batrachochytrium dendrobadis in larval ambystomad
salamanders. Herpetological Conservaon Biology 5, 174–
182.
Woodhams, D.C., Alford, R.A. & Marantelli, G. (2003). Emerging
disease of amphibians cured by elevated body temperature.
Diseases of Aquac Organisms 55, 65–67.
Woodhams, D.C., Geiger, C.C., Reinert, L.K., Rollins-Smith, L.A.,
Lam, B., Harris, R.N., Briggs, C.J., Vredenburg, V.T. &
Voyles, J. (2012). Treatment of amphibians infected with
chytrid fungus, learning from failed trials with itraconazole,
anmicrobial pepdes, bacteria, and heat therapy. Diseases
of Aquac Organisms 98, 11–25.
Accepted: 12 February 2018
C. Michaels et al.


... 2,20 B. dendrobatidis has been shown to infect Taricha granulosa in the wild 29 and has been reported in captive-bred axolotls. 11,12,23 In addition, B. dendrobatidis can infect larval zebrafish, 19 creating potential concerns for spread between aquatic animal models when an outbreak is detected within a laboratory setting. ...
... andersoni, A. dumerilii, and A. mexicanum) involved bathing the animals with 0.005% to 0.01% itraconazole across several treatment durations. 23 Surprisingly, mortality for axolotls (A. mexicanum) varied widely, with no loss of animals treated at one location and 100% mortality at another. ...
... The mortality rate for the axolotls in our laboratory (2 of 46 animals; 4.3%) was much higher than would be expected during a similar colony time period outside of disease treatment but was low compared with that described previously. 23 This difference may be related to the use of a relatively low (0.002% to 0.0025%) concentration of itraconazole in the protocol we described here. ...
Article
Full-text available
Chytridiomycosis is an infectious disease of amphibians caused by the fungal species Batrachochytrium dendrobatidis and B. salamandrivorans and has been implicated in the population decline of amphibian species worldwide. This case report describes a successful treatment protocol for chytridiomycosis in laboratory-maintained colonies of axolotls (Ambystoma mexicanum) and rough-skinned newts (Taricha granulosa). Over 12 mo, axolotls (n = 12) in a laboratory-reared colony developed multifocal erythematous dermatitis, mainly on the distal limbs and tails. Wild-caught newts handled by the same labpersonnel were housed in an adjacent room and occasionally presented with abdominal distension and lethargy. Differentials included poor water quality, pathogen infection, parasitic infestation, and trauma. Antibiotic treatment of animals according to results of bacterial culture and sensitivity, combined with bleach disinfection of aquaria, did not resolve clinical signs. Skin swabs from clinically affected axolotls submitted for a newly available commercial screen were positive for B. dendrobatidis. Additional PCR and sequencing analysis revealed chytrid-positive animals among group-housed newts in 2 clinically unaffected aquaria and suspected PCR-positives for 2 affected newt aquaria and an additional axolotl. Axolotls with skin lesions(n = 2) and newts with abdominal distension and lethargy (n = 2) underwent experimental treatment with itraconazole submersion (0.002% to 0.0025%; 5 min daily for 10 d). This pilot treatment was well tolerated and led to clinical resolution. Subsequent itraconazole treatment of the entire colony led to regrowth of extremities and restoration of normal coloration among axolotls. During treatment, the facility was decontaminated, and additional biosecurity measures were developed. PCR results after the pilot treatment and subsequent full-colony treatments (at 1 wk, 1 mo, and 6 mo after treatment) were negative for the presence of B. dendrobatidis. Because chytridiomycosis is a reportable animal disease in our state, colonies officially remained quarantined until negative PCR results were obtained at least 6 mo after treatment.
... Ambystoma dumerilii are known to be capable of carrying Batrachochytrium dendrobatidis (Bd) without displaying signs of clinical disease (Michaels et al., 2018), therefore it is of utmost importance that adequate testing is undertaken when acquiring new individuals into an established collection. Bd loads in the salamanders can be very low which can affect detection rates. ...
... When swabbing this species for Bd, particular attention should be paid to the keratinised mouthparts, as these act as focal areas for Bd and Bsal and therefore aid in an increased detection rate (see Appendix 3.2). If specimens of A. dumerilii test positive for Bd, chemical antifungal treatments may be used to clear infection following methodology detailed by Michaels et al. (2018). ...
... Enclosure use and design Cikanek et al., 2014;Mannings et al., 2023Nutrition Antwis, Preziosi & Fidgett, 2014Dierenfeld & King 2008;Dugas, Yeager & Richards-Zawacki, 2013;Edwards et al., 2017;Keogh et al., 2018;McInerney, Silla & Byrne, 2019;Michaels et al., 2021;Newton-Youens, Michaels & Preziosi, 2022;Ogilvy, Preziosi & Fidgett, 2012;Rodríguez & Pessier, 2014;Silla, McInerney & Byrne, 2016;Stückler et al., 2022;Venesky et al., 2012 Provision of appropriate lighting Antwis & Browne, 2009;Baines et al., 2016;Michaels, Antwis & Preziosi, 2015;Shaw et al., 2012;Verschooren et al., 2011; Provision of enrichment Michaels, Downie & Campbell-Palmer, 2014 Behavioural syndromes See review in Kelleher, Silla & Byrne, 2018 Artificial manipulation of seasonally dependent adaptations (brumation, aestivation, torpor) Calatayud et al., 2015;Calatayud et al., 2020 Water quality and larval rearing techniques Behr & Rödder, 2018;Ciani et al., 2018;Fenolio et al., 2014;Gawor et al., 2012;Gower et al., 2012;Higgins et al., 2021;Lassiter et al., 2020;Michaels, Antwis & Preziosi, 2014;Pasmans et al., 2012 Health assessment Davis & Maerz, 2011;Narayan & Hero, 2011;Narayan, Hero & Cockrem, 2012Substrates Tapley et al., 2014 Disease treatment protocols and pathogen management Brannelly, Richards-Zawacki & Pessier, 2012;Garner et al., 2009;Martel et al., 2011;Michaels et al., 2018;Rendle et al., 2015;Ujszegi et al., 2021Microbiome Becker et al., 2014Fieschi-Méric et al., 2023;Micahels, & Preziosi, 2020;Michaels, 2022 Welfare Boultwood, O'Brien & Rose, 2021;Brod, Brookes & Garner, 2019;Carter, et al., 2021;Dias et al., 2022;Graves, Dias & Michaels, 2023;Holmes et al., 2016;Holmes et al., 2018;Ramos & Ortiz-Díez, 2021;Slight, Nichols & Arbuckle, 2015 Pre-translocation training Crane & Mathis, 2011 Assisted reproductive techniques and biobanking See Chapter 12 amphibian conservation action plan: a status review and roadmap for global amphibian conservation environmental adaptation is necessary as not all species will respond to inbreeding and artificial selection uniformly (Grueber et al., 2015). Suboptimal captive husbandry may also result in individuals with lower phenotypic fitness that are less likely to establish in wild habitats following translocation. ...
Chapter
Full-text available
In the face of overwhelming and sometimes acute threats to many amphibians, such as disease or habitat destruction, the only hope in the short-term for populations and species at imminent risk of extinction is immediate rescue for the establishment and management of captive survival-assurance colonies (CSCs). Such programmes are not the final solution for conservation of any species, but in some circumstances may be the only chance to preserve the potential for eventual recovery of a species or population to threat-ameliorated habitat. A captive assurance strategy should always be implemented as part of an integrated conservation plan that includes research on amphibian biology, advances in husbandry and veterinary care, pathology, training and capacity-building in range countries, mitigation of threats in the wild, and ongoing habitat and species protection and, where appropriate, disease risk analysis and translocation. The existence of captive colonies also facilitates many of the goals of other ACAP branches, including research on amphibians and their diseases as well as the development and validation of methods that may be later used in the field. Captive programmes do not replace important programmes related to, inter alia, habitat preservation, control of harvesting, climate change, and ecotoxicology, but instead provide options and resources to enable survival of some species while these research programmes proceed, and to directly or indirectly support such programmes.
... This species lives only in high mountain streams in Estado de México, Michoacán, and Guerrero (Woolrich-Piña et al. 2017), where habitat loss, pollution and introduced predatory fish are the principal threats to its conservation (Shaffer et al. 2008b). Ambystoma dumerilii occur only at Pátzcuaro Lake in Michoacán and the presence of Bd in captive individuals was reported previously by Michaels et al. (2018) from a colony in the London Zoo, UK. Since 2003 this species has been in serious decline, and in 2008 was declared to be close to extinction (Shaffer et al. 2008a). ...
... This species lives only in high mountain streams in Estado de México, Michoacán, and Guerrero (Woolrich-Piña et al. 2017), where habitat loss, pollution and introduced predatory fish are the principal threats to its conservation (Shaffer et al. 2008b). Ambystoma dumerilii occur only at Pátzcuaro Lake in Michoacán and the presence of Bd in captive individuals was reported previously by Michaels et al. (2018) from a colony in the London Zoo, UK. Since 2003 this species has been in serious decline, and in 2008 was declared to be close to extinction (Shaffer et al. 2008a). ...
Article
Full-text available
Most of Ambystoma species in Mexico are endemic having a limited distribution, and are threatened principally by anthropogenic factors. The presence of pathogens as Batrachochytrium dendrobatidis could be another threat to these species, especially in species with limited range. We surveyed populations of Ambystoma andersoni, A. flavipiperatum, and A. rivulare to test for the presence of B. dendrobatidis. We also examined specimens of Ambystoma dumerilii from captive populations. Using real-time PCR assays we found evidence of B. dendrobatidis in all Ambystoma species tested.
Chapter
Laboratory animal health monitoring programs are necessary to protect animal health and welfare, the validity of experimental data, and human health against zoonotic infections. Health monitoring programs should be designed based on a risk assessment and knowledge about the biology and transmission of salamander pathogens. Both traditional and molecular diagnostic platforms are available for salamanders, and they provide complementary information. A comprehensive approach to health monitoring leverages the advantages of multiple platforms to provide a more complete picture of colony health and pathogen status. This chapter presents key considerations in the design and implementation of a colony health monitoring program for laboratory salamanders, including protocols for necropsy and sample collection.Key wordsSalamanderAxolotlHealth monitoringBiosecurityQuarantineNecropsyPathologyPathogenParasiteEnvironmental monitoring
Article
Full-text available
Chytridiomycosis, an emerging disease caused mostly by the pathogen Batrachochytrium dendrobatidis, has caused massive amphibian population declines and extinctions worldwide. The ecology of this disease is mainly explained by the interaction of environmental factors, pathogen biology, and host traits including development. For paedomorphic salamanders, differences in B. dendrobatidis infection may be explained by metamorphosis and water physicochemical conditions. In this study, we aimed to determine the influence of environmental and host factors on B. dendrobatidis prevalence and infection intensity in the facultative paedomorphic salamander Ambystoma altamirani. We determined B. dendrobatidis prevalence and infection load in four populations of A. altamirani along 1 year (four seasons) and assessed their relationship with environmental factors and host metamorphic status (gilled or non‐gilled). We found that B. dendrobatidis prevalence and infection load are largely explained by metamorphic status and environmental factors such as elevation, seasonality, water temperature, pH, conductivity, and dissolved oxygen. To our knowledge, this is the first study to empirically show the effect of metamorphosis on B. dendrobatidis infection status across locations and seasons. This information may be used to understand the temporal dynamics of B. dendrobatidis–host interactions and to identify potential disease outbreaks that may cause cryptic sublethal effects on salamander populations. Our results will help in the development of conservation strategies for paedomorphic salamanders that are already considered threatened by anthropogenic factors such as habitat loss and climate change.
Article
In 2019, two wild-caught adult female eastern hellbenders (Cryptobranchus alleganiensis alleganiensis) received a preshipment examination and were individually swabbed for chytrid testing via quantitative polymerase chain reaction (qPCR). Physical examination was unremarkable. Both females tested positive for Batrachochytrium dendrobatidis (Bd) and negative for B. salamandrivorans (Bsal). A course of terbinafine hydrochloride 1% in alcohol was administered in a 0.005% treatment bath for 5 min once daily for 5 d. Both animals were individually retested 1, 3, and 4 wk after treatment using qPCR. All post-treatment samples were negative for Bd and Bsal. This report represents the first successful treatment with terbinafine hydrochloride 1% in alcohol to eliminate subclinical Bd infection in eastern hellbenders and underlines the importance of preshipment testing for chytrid in all amphibians being transferred to new facilities or released into the wild as a means to minimize risk of disease introduction via subclinically infected individuals.
Article
The Class Amphibia consists of three extant orders: Anura (frogs and toads), Caudata (salamanders) and Gymnophiona (caecilians). Commonly kept species include the White's tree frog (Ranoidea caerulea), African clawed frog (Xenopus laevis) and Argentine horned frog (Ceratophrys ornata). The amphibian pet trade has been implicated in the global spread of amphibian infectious disease and has contributed to amphibian population declines. Visual examination is recommended prior to handling, preferably in the animal's transport carrier to minimise disturbance. For diagnostic tests, this chapter includes blood sampling; faecal analysis; skin swabs, scrapes, and smears; nutritional support; fluid therapy; anaesthesia and analgesia, and euthanasia. It discusses common medical and surgical conditions, non‐infectious diseases, diagnostic imaging, preventative health measures, and medications and formulary in the Amphibians.
Article
This article updates the understanding of two extirpation-driving infectious diseases, Batrachochytrium dendrobatidis and Batrachochytrium salamandrivorans, and Ranavirus. Experimental studies and dynamic, multifactorial population modeling have outlined the epidemiology and future population impacts of B dendrobatidis, B salamandrivorans, and Ranavirus. New genomic findings on divergent fungal and viral pathogens can help optimize control and disease management strategies. Although there have been major advances in knowledge of amphibian pathogens, controlled studies are needed to guide population recovery to elucidate and evaluate transmission routes for several pathogens, examine environmental control, and validate new diagnostic tools to confirm the presence of disease.
Article
Full-text available
The amphibian chytrid fungi, Batrachochytrium dendrobatidis (Bd) and B. salamandrivorans (Bsal), pose a major threat to amphibian biodiversity. Recent evidence suggests Southeast Asia as a potential cradle for both fungi, which likely resulted in widespread host-pathogen co-existence. We sampled 583 salamanders from 8 species across Vietnam in 55 locations for Bsal and Bd, determined scaled mass index as a proxy for fitness and collected environmental data. Bsal was found within 14 of the 55 habitats (2 of which it was detected in 2013), in 5 salamandrid species, with a prevalence of 2.92%. The globalized pandemic lineage of Bd was found within one pond on one species with a prevalence of 0.69%. Combined with a complete lack of correlation between infection and individual body condition and absence of indication of associated disease, this suggests low level pathogen endemism and Bsal and Bd co-existence with Vietnamese salamandrid populations. Bsal was more widespread than Bd, and occurs at temperatures higher than tolerated by the type strain, suggesting a wider thermal niche than currently known. Therefore, this study provides support for the hypothesis that these chytrid fungi may be endemic to Asia and that species within this region may act as a disease reservoir.
Article
Full-text available
The cutaneous microbiota plays a significant role in the biology of their vertebrate hosts, and its composition is known to be influenced both by host and environment, with captive conditions often altering alpha diversity. Here, we compare the cutaneous bacterial communities of 61 amphibians (both wild and captive) from Hiroshima, Japan, using high-throughput amplicon sequencing of a segment of the 16S rRNA gene. The majority of these samples came from a captive breeding facility at Hiroshima University where specimens from six species are maintained under highly standardized conditions for several generations. This allowed to identify host effects on the bacterial communities under near identical environmental conditions in captivity. We found the structure of the cutaneous bacterial community significantly differing between wild and captive individuals of newts, Cynops pyrrhogaster, with a higher alpha diversity found in the wild individuals. Community structure also showed distinct patterns when comparing different species of amphibians kept under highly similar conditions, revealing an intrinsic host effect. Bacterial communities of dorsal vs. ventral skin surfaces did not significantly differ in most species, but a trend of higher alpha diversity on the ventral surface was found in Oriental fire-bellied toads, Bombina orientalis. This study confirms the cutaneous microbiota of amphibians as a highly dynamic system influenced by a complex interplay of numerous factors.
Article
Full-text available
Emerging fungal diseases can drive amphibian species to local extinction. During 2010-2016, we examined 1,921 urodeles in 3 European countries. Presence of the chytrid fungus Batrachochytrium salamandrivorans at new locations and in urodeles of different species expands the known geographic and host range of the fungus and underpins its imminent threat to biodiversity.
Article
Full-text available
A newly identified fungal pathogen, Batrachochytrium salamandrivorans(Bsal), is responsible for mass mortality events and severe population declines in European salamanders. The eastern USA has the highest diversity of salamanders in the world and the introduction of this pathogen is likely to be devastating. Although data are inevitably limited for new pathogens, disease-risk assessments use best available data to inform management decisions. Using characteristics of Bsalecology, spatial data on imports and pet trade establishments, and salamander species diversity, we identify high-risk areas with both a high likelihood of introduction and severe consequences for local salamanders. We predict that the Pacific coast, southern Appalachian Mountains and mid-Atlantic regions will have the highest relative risk from Bsal. Management of invasive pathogens becomes difficult once they are established in wildlife populations; therefore, import restrictions to limit pathogen introduction and early detection through surveillance of high-risk areas are priorities for preventing the next crisis for North American salamanders.
Article
Full-text available
Chytridiomycosis is a disease of amphibians caused by the fungus Batrachochytrium dendrobatidis (Bd), which colonizes keratinized tissues in adult and larval amphibians. Considerable progress has been made in understanding the host-pathogen ecology of Bd in larval anurans, yet little is known about how Bd affects larval salamanders. Because the structure of keratinized jaw sheaths in Ambystoma larvae have not been thoroughly documented, we first described the structure in three species of larval Ambystoma. We then conducted a laboratory experiment to test if Bd affects growth and developmental rates of larval Marbled Salamanders (Ambystoma opacum). We observed keratinized jaw sheaths in all three species of Ambystoma, but the sheath was not present in all individuals. In our exposure experiment, none of the A. opacum, whose mouthparts were screened for Bd, tested positive, nor was there an effect of Bd on larval life-history responses. A cautionary note, however, is that although our method of Bd infection has been successful in other amphibian-Bd experiments in our laboratory, our exposure experiment did not include a positive control of other taxa known to become infected with Bd. We are uncertain why none of the larval A. opacum became infected with Bd, given that we observed keratinized jaw sheaths in this species. Two possible explanations are the keratinized jaw sheaths of larval Ambystoma differ among species in structure or keratin type so that Bd may not be able to successfully infect them or, A. opacum larvae may have cleared low intensity Bd infections prior to metamorphosis.
Article
Full-text available
Batrachochytrium dendrobatidis (Bd) is the causative agent of the disease amphibian chytridiomycosis, one of the factors driving amphibian population declines. Bd infections are treatable in at least some cases, but in the Gymnophiona has been little reported, and restricted to heat treatment in the form of increased environmental temperature. We report the successful treatment of Bd infection in the terrestrial African caecilian Geotrypetes seraphini and the prophylactic treatment of the aquatic neotropical caecilian Potomotyphlus kaupii, using 30 minute immersions in a 0.01% solution of the antifungal itraconazole over a period of 11 days. Previously only recorded in wild African Gymnophiona, our report of Bd in P. kaupii is not only the first record of infection in a wild aquatic caecilian but also in a caecilian of neotropical origin. To improve our understanding of the impact of Bd on caecilians, Bd isolates should be obtained from wild caecilians in order to ascertain what lineages of Bd infect this order. In addition, more wild individuals should be subjected to Bd diagnostic surveys, including in Asia where caecilians have not yet been subject to such surveys.
Article
Full-text available
Chytridiomycosis caused by the chytrid fungus Batrachochytrium salamandrivorans (Bsal) poses a serious threat to urodelan diversity worldwide. Antimycotic treatment of this disease using protocols developed for the related fungus Batrachochytrium dendrobatidis (Bd), results in therapeutic failure. Here, we reveal that this therapeutic failure is partly due to different minimum inhibitory concentrations (MICs) of antimycotics against Bsal and Bd. In vitro growth inhibition of Bsal occurs after exposure to voriconazole, polymyxin E, itraconazole and terbinafine but not to florfenicol. Synergistic effects between polymyxin E and voriconazole or itraconazole significantly decreased the combined MICs necessary to inhibit Bsal growth. Topical treatment of infected fire salamanders (Salamandra salamandra), with voriconazole or itraconazole alone (12.5 μg/ml and 0.6 μg/ml respectively) or in combination with polymyxin E (2000 IU/ml) at an ambient temperature of 15 °C during 10 days decreased fungal loads but did not clear Bsal infections. However, topical treatment of Bsal infected animals with a combination of polymyxin E (2000 IU/ml) and voriconazole (12.5 μg/ml) at an ambient temperature of 20 °C resulted in clearance of Bsal infections. This treatment protocol was validated in 12 fire salamanders infected with Bsal during a field outbreak and resulted in clearance of infection in all animals.
Article
Full-text available
Amphibian chytridiomycosis, caused by the fungus Batrachochytrium dendrobatidis ( Bd ), has been implicated in the decline and extinction of amphibian species worldwide, in addition to catastrophic losses of animals in captivity. Conservation of threatened amphibians, including captive breeding and maintenance of animals in zoos, research facilities, and private collections, requires effective control of pathogens. Several chemical compounds, including Formalite III ® , itraconazole, and chloramphenicol, have been used to treat amphibians infected with Bd , with varying levels of success. Here, we report successful clearance of Bd in five species of post-metamorphic anurans and one caudate species using terbinafine hydrochloride (HCl) in alcohol, which is available over the counter as Lamisil AT™ (Novartis Pharmaceuticals Inc., New York, NY). Treatments consisting of 5 min soak in fresh 0.01% or 0.005% terbinafine HCl in alcohol for either five consecutive days or for six treatments spread across 10 days successfully cleared Bd from 100% of 81 test subjects in eight trials. Our results indicate that terbinafine HCl in alcohol has a high therapeutic index as a treatment for Bd infection in living post-metamorphic amphibians.
Article
The impacts of pathogen emergence in naïve hosts can be catastrophic, and pathogen spread now ranks as a major threat to biodiversity. However, pathogen impacts can persist for decades after epidemics and produce variable host outcomes. Chytridiomycosis in amphibians (caused by the fungal pathogen Batrachochytrium dendrobatidis, Bd) is an exemplar, with impacts ranging from rapid population crashes and extinctions, to population declines and subsequent recoveries. Here, we investigate long-term impacts associated with chytridiomycosis in Australia. We conducted a continent-wide assessment of the disease, reviewing data collected since the arrival of Bd in about 1978, to assess and characterize mechanisms driving past, present and future impacts. We found chytridiomycosis to be implicated in the extinction or decline of 43 of Australia's 238 amphibian species. Population trajectories of declined species are highly variable; six species are experiencing ongoing declines, eight species are apparently stable and 11 species are recovering. Our results highlight that while some species are expanding, Bd continues to threaten species long after its emergence. Australian case-studies and synthesis of the global chytridiomycosis literature suggests that amphibian reservoir hosts are associated with continued declines in endemically infected populations, while population stability is promoted by environmental conditions that restrict Bd impact, and maintenance of high recruitment capacity that can offset mortality. Host genetic adaptation or decreased pathogen virulence may facilitate species recovery, but neither has been empirically demonstrated. Understanding processes that influence Bd-host dynamics and population persistence is crucial for assessing species extinction risk and identifying strategies to conserve disease-threatened species.