Evidence of a chytrid fungus infection involved in the decline of the common midwife toad (Alytes obstetricans) in protected areas of central Spain
Introduction
Declines of amphibian populations in their natural habitats, with no identifiable direct causes, have become a subject of increasing concern for the scientific community in recent years (Blaustein and Wake, 1990, Wake, 1991, Blaustein, 1994, McCoy, 1994). It is a complex problem with multiple potential causes whose relative importance in local extinction processes has yet to be established, as well as the extent to which these factors affect normal population dynamics of amphibians (Pechman et al., 1991, Alford and Richards, 1999). Several studies have provided solid evidence of disappearances of populations that were common only a few decades ago, particularly in montane, well conserved habitats (Bradford, 1991, Carey, 1993, Richards et al., 1993, Lips, 1998). Some of these studies have implicated abiotic agents in the declines, mostly physical changes in the environment which act as stressing factors affecting normal physiological functions of the amphibians (Bradford et al., 1992, Blaustein et al., 1994). Biotic factors have also been implicated in some cases, as in the recent description of a pathogenic fungus which has been causally related to amphibian population declines in Australia and Northern, Central and South America (Berger et al., 1998, Daszak et al., 1999, Pessier et al., 1999). This fungus belongs to the order Chytridiales, and has been included in a new genus, Batrachochytrium (Longcore et al., 1999). It is waterborne and pathogenic to adult amphibians, although it does not kill tadpoles; it prefers cooler temperatures, and is not solely dependent upon the highly susceptible host species for its continued existence (Berger et al., 1999a). Chytrids were not known to parasitise vertebrates prior to these studies.
Chytridiomycosis is a fatal disease which has been identified in an increasing number of amphibian species, as preserved material from populations affected some years ago is being re-studied. The disease can be carried by healthy tadpoles and has also been found in a small proportion of apparently healthy frogs and tadpoles (Berger et al., 1999a). In post-metamorphic amphibians it causes a widespread infection of the skin, resulting in hyperkeratosis, sloughing and erosions of the epidermis, and occasional ulcerations (Berger et al., 1999a).
No fungal infections causing amphibian declines have been reported so far in Europe, and such declines have mainly occurred as a result of conventional reasons associated with habitat loss and disturbance (e.g. Cooke, 1972, Beebee, 1977, Kuzmin, 1994, Cunningham et al., 1996). Unlike other parts of the world, no species in Europe has gone extinct recently, and the cases of apparently inexplicable declines are very unusual (e.g. Semb-Johansson, 1992).
In Spain, a recent case was observed in July 1992 and 1994, when two episodes of mass mortality of larval and metamorphic common midwife toads (Alytes obstetricans) were recorded in a lake in the Pyrenean Mountains (Márquez et al., 1995). In that case, the bacterium Aeromonas hydrophila, which produces a disease commonly known as “red leg”, was shown to be responsible for the mortality.
In the summers of 1997 and 1998, thousands of dead, post-metamorphic A. obstetricans were found around the ponds in the Peñalara Natural Park in central Spain. They had an apparently healthy general aspect, showing no traces of red-leg infection. Dead tadpoles or adults were not found. A limnological study was performed during the summer of 1998 in which 25 water chemistry variables were measured in selected ponds, and a rare increase in pH (up to 9) in some of the ponds was reported (Toro and Granados, personal communication). In the summer of 1999 we carried out a study of the A. obstetricans population to detect the potential causes of the mass mortality in order to act as soon as possible to ensure the conservation of the populations, which are isolated from other populations in central Spain (Garcı́a-Parı́s, 1995).
Section snippets
Study area and biology of A. obstetricans
The Peñalara Natural Park is an alpine area in central Spain, very close to Madrid. The area has been protected for 70 years and, in spite of the high number of visitors (>100 000 per year), conservation and restoration practices maintain its preservation status and ecological health in good condition. The area is located at about 2000 m of elevation, and mainly consists of bogs and alpine grasslands with granitic outcrops. The Natural Park holds >250 ponds from 0.3 to 6463 m2 in area (average
Methods
During the summer of 1999 (June–September) we extensively sampled every pond of the Peñalara Natural Park at least six times, in search of amphibian larvae. In addition, we searched for adults in the surroundings of the ponds by day (when they hide under rocks) or at dawn (when they can be detected by listening for male choruses). We compared the data with previous results obtained during the summers of 1981–1986 by the third author (Garcı́a-Parı́s and Martı́n, 1987, and unpublished data).
Dead
Results
In the past decade A. obstetricans tadpoles were present in at least 35 ponds, which constitute 44% of the ponds sampled before 1999. In 1999 they were present in only five ponds across the Natural Park; i.e. they had disappeared from 86% of the ponds that were occupied a few years ago (Fig. 1). Although we do not have precise quantitative density data from the past, the estimated tadpole density has decreased sharply in three of the five ponds that still maintained tadpoles in 1999, when
Discussion
Sudden episodes of massive death of post-metamorphic individuals suggest that the observed decline has been caused by an epidemic disease, and clearly exclude the possibility of natural population fluctuations. Other causes, as for example human impacts, were not examined but, do not seem probable in this case. A. obstetricans was one of the most abundant amphibian species in the Park in the past, not only in the relatively high number of ponds used for reproduction, but also with respect to
Acknowledgements
The Consejerı́a de Medio Ambiente de la Comunidad de Madrid funded the study “Inventario de los Anfibios de Peñalara”. Special thanks to Juan Vielva, director of the Peñalara Natural Park, as well as the rest of the people working on the Park for facilities provided. The authors are also grateful to M. Alcobendas, B. Arconada, M. Valladolid, J. Bedoya and C. Cummins for critical comments and help, and especially to L. Berger. I. Martı́nez-Solano is supported by a pre-doctoral fellowship from
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