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First record of Saprolegnia sp. in an amphibian population in Colombia.


The study of the decline of amphibian populations in Colombia has focused on the morphological evaluation of the fungal pathogen Batrachochytrium dendrobatidis (1, 2). However, several authors have found that this pathogen is not solely responsible for the decline of amphibians (3, 4). Saprolegnia is a pathogen common in fish populations and has been found in some amphibian populations around the world (5). Saprolegnia has been recognized for years as a major eukaryotic pathogen of freshwater fish, distributed worldwide (6). It causes mortality in fish farms, due to its ability to colonize the eggs and fish in early developmental stages, infect wounds and penetrate the epidermis using enzymes or mycelium. When host defenses are low, infection may produce an osmotic imbalance, other infections, and respiratory failure as a result of primary or opportunistic infection (7). Saprolegnia has many species with different morphological, physiological and genetic characteristics which give varying levels of virulence and apparently uses multiple hosts (8). The ability of Saprolegnia to produce hydrolytic enzymes that allow the mycelium to penetrate the epidermis of the host causes tissue damage, production of toxins and imbalance of body fluids. As a result, Saprolegnia spp. are multihost infectious agents in different species of fish, frogs and salamanders (9, 10).

Blaustein et al. (4) studied the presence of the fungus Saprolegnia ferax. They identified it as responsible for the mortality of amphibian larvae in the mountains of Oregon, USA. Kiesecker and Blaustein (3) identified the interaction between UV and Saprolegnia ferax, showing a reduction in the number of eggs in two frog species (Anaxyrus boreas and Rana cascadae). They also studied the incidence of this fungus on egg mortality in some amphibian species in north western United States. Kiesecker et al. (5) obtained experimental evidence for the role of rainbow trout (Oncorhynchus mykiss) in the transmission of S. ferax in populations of the toad Anaxyrus boreas. They demonstrated how fish farms act as vectors and increase the mortality of amphibians in different environmental conditions. In 2002, Blaustein and Kiesecker (10) confirmed that a major cause of larval mortality in local populations of some amphibian species in North America is the oomycete fungus S. ferax. They also found that the widespread occurrence of this fungus among these populations and geographic regions may be the result in differences in their degree of virulence. Blaustein et al. (11) suggested that some pollutants, such as fertilizers, heavy metals, PHAs and other toxic chemicals may have a synergistic influence on the fungal-amphibian relationship. The same author indicated that embryos exposed to high levels of UV-B resulted with an increased mortality by S. ferax. Carey and Alexander (12) classified S. ferax as an infectious disease causing the decline of amphibian populations as well as increase in natural areas due to climate change; for instance, low levels of rainfall caused by the "El Nino" phenomenon increased the effect of UV-B. Daszak et al. (13) noted the need to develop timing analyses of the incidence of saprolegnosis. Collins and Storfer (14) indicated that transmission of S. ferax may increase due to the introduction of foreign species which act as reservoirs for the fungus affecting native species.

Scientific reports of this pathogen in South American amphibians do not exist. There are reports restricted to commercial fish, e.g. there are some records of S. parasitica in fish fauna in Argentina and Chile. Consequently, there is no information available regarding its potential role as a causal agent and its mode of transmission in amphibians in South America (15).

In Colombia, the introduction of non-native species into ecosystems has been increasing in recent years. Changes in amphibian populations dependent upon lotic waters by direct competition from non-native species are likely, perhaps including populations of the montane frogs Atelopus muisca and A. lozanoi in Chingaza National Park, or populations of A. mittermeieri in the Alto Rio Fonce Flora and Fauna Sanctuary; all of them are locations where rainbow trout has been reported (1).

Such practices may have potentially enabled the introduction in Colombia of new pathogens such as Saprolegnia, which moves from different hosts that share the same habitats as the introduced fish Oncorhynchus mykiss, Oreochromis spp., Piaractus brachypomus, Pimelodus clarias and native species such as Eremophilus mutisii, the latter endemic to the Cundinamarca-Boyaca high plain in the Eastern Cordillera of Colombia (16, 17, 18).

The present study reports the discovery of the pathogen (Saprolegnia sp.) affecting an amphibian population in Colombia. The fungus was detected in a population of Atelopus mittermeieri which had been previously reported to be infected with Batrachochytrium dendrobatidis (2). Infection by Saprolegnia sp. represents a possible interspecific transmission event caused by the presence of rainbow trout. If this is confirmed, then it is possible that the decline of amphibians in this site is not attributed to the presence of a single pathogen, but to additional organisms and factors.

Materials and methods

The fungus was detected by microscopic observation using the imprinting technique on lactophenol-blue stain on integumentary scrapings from the hind limbs of 37 specimens of Atelopus mittermeieri. Specimens previously had been fixed in 10% formalin and preserved in 70% ethanol after being collected from the wild. Specimens are deposited in the reference collection of amphibians of the museum of the Pontificia Universidad Javeriana (MUJ). Glass microscope slides were prepared and microscopic observations were done with objective lens magnifications at 4x, 10x, 40x and 100x. The identification of the fungus was aided with the taxonomic keys of Seymour (19). Morphological characteristics were described at the microscopic level. For each slide on which hyphae were observed, we made a description of pigments in the hyphal body, hyphae form, presence of septa and reproductive structures (zoosporangia). These observations allowed for the morphological identification of the genus. Since our samples were preserved in formalin, it was not possible to conduct a molecular identification or use microbiological techniques based on cultures of the fungus. Information on temperature and humidity of the habitat, where positive samples were obtained, was collected from notes accompanying specimens obtained during field monitoring of Atelopus mittermeieri populations between 2005 and 2007 in Aguas Claras creek, a tributary of the Rio Negro, in the Rio Negro basin in the Guanenta Alto Fonce Flora and Fauna Sanctuary, Department of Santander (Figure 1). Data points of the infected specimens were recorded with a data logger TrendReader Express[R] (Figure 2). Specimen MUJ 4367 was obtained between days 25 and 27 of September 2006, at an elevation of 2,900 m; specimen MUJ 4358 was obtained in June 2005 at an elevation of 2,525 m.


During field monitoring of Atelopus mittermeieri between 2005-2006 in Aguas Claras creek, a tributary of the Rio Negro, in the Rio Negro basin in the Guanenta Alto Fonce Flora and Fauna Sanctuary in the Department of Santander, some specimens of this species were found dead with some external signs of fungal infection on ventral surfaces of their thighs (Figures 3 and 4). These specimens were preserved in formalin.

Additionally, during surveys for amphibian chytridiomycosis in Colombia, it was decided to evaluate these samples by histological observation of Batrachochytrium dendrobatidis (previously reported by Ruiz and Rueda in 2008 (2) in the same population of amphibians). Because of these two reasons, those particular specimens were examined in more detail.

Studying the same specimens collected and reported in 1998 using a scraping technique, previous determinations of infection by Batrachochytrium dendrobatidis were confirmed, and additional infection by Saprolegnia was identified.

Microscopic evaluation of the growth of the fungal bodies revealed the presence of thin somatic hyaline hyphae, without septa and with few branches. It additionally revealed an extensive and dense mycelium near the substrate (Figure 5). At a higher magnification (40x), the presence of long and cylindrical reproductive structures was observed (oosporangia), which were separated from the basal somatic hyphae by a small septum.

Oosporangia are 160-220 [micro]m in size, clavate form, thick, and with a smooth wall. Spores are spherical and subglobose, and were observed in a compact catenula arrangement within the sac or sporangia (fungal propagules) (Figure 5).



This study reports for the first time the presence of the oomycete fungus Saprolegnia sp. in a population of the highland frog Atelopus mittermeieri. Since it was found in association with the chytrid fungus B. dendrobatidis, it is noteworthy that two quite unrelated species of pathogenic fungi are affecting amphibian species in Colombia.

Of a total of 37 adult specimens examined from the reference collections, only two of the specimens showed hyphal growth (Figure 4). One of the infected amphibians (MUJ 4367) was found dead on the side of the Aguas Claras creek (Figure 3) with advanced hyphal growth. Air temperature was between 11.77[degrees]C and 20.55[degrees]C, relative environmental humidity ranged from 53% to 99% (85.73% on average), and water temperature was between 9[degrees]C and 14[degrees]C (Figure 2). The second specimen (MUJ 4358) was an adult male and was found dead during the second sampling of this species, with no apparent evidence of hyphal growth.

A more detailed analysis of the incidence of this fungus on adult specimens of Atelopus mittermeieri was recorded in a transect at the same site in June 2005. Presence of the pathogen in the specimen MUJ 4358 (Figure 4) was found. In the same transect another four specimens were observed, two amplectant individuals were apparently healthy. In another assessment at the same linear distance, three specimens were reported with chytridiomycosis in September 2006; presence of the pathogen Saprolegnia sp. was observed only in the specimen MUJ 4367 found dead in the creek (Figure 3).

The infected frogs were found in Aguas Claras creek co-occurring with rainbow trout (Oncorhynchus mykis), a finding that suggests a possible vertical transmission of this pathogen among species. During the discovery of dead specimens of A. mittermeieri we observed that mycelia had a grayish white colour around the body, especially in the legs. Apparently it was a localized infection because the mycelial growth was observed attached to the limbs skin or hanging from the same skin. In addition, infection was observed in one dead specimen that was missing the right leg (MUJ 4367), and the second specimen infected (MUJ 4358) was in poor physical condition and low weight.

A new survey of three days of search in March 2010 resulted in the discovery of a single specimen of A. mittermeieri without symptoms of the disease. We were able to obtain and evaluate several specimens of rainbow trout with negative results. We could also find with the help of locals that introduction of trout was initiated over 30 years ago, upstream in Chontales creek within the same basin of Aguas Claras creek. The few data available allow us to make a preliminary assessment on the prevalence of Saprolegnia on local populations of Atelopus, but future studies with this population can be further improved, as well as a specific investigation into the possibility of vertical transmission of Saprolegnia between trout and Atelopus (or other amphibians).





The decline of amphibians is the result of a complexity of environmental factors that generate variation in the habitat of amphibians (10). Furthermore, other agents may accelerate the decline of amphibians. Examples of this are emerging infectious diseases (13). The most studied disease is chytridiomycosis; however, it is not the only one and does not necessarily act alone in amphibian populations. Amphibians can also be affected by other diseases, such as those caused by different species of the fungal genus Saprolegnia which may be considered a secondary disease (5, 18). Therefore, research should be carried out in other infectious agents that directly or indirectly affect amphibian communities.

It has been discussed that interspecies vertical transmission may occur with this fungus: amphibians have a pathogenic fungus prevalent in fish and widely studied in different species of rainbow trout (20). Fungi of the genus Saprolegnia, which usually occur when the host immune system is suppressed or compromised, cause most superficial fungal infections affecting fish (21). This fact could had occurred at our study site because specimens were missing limbs or appeared thin and weak, which affect the immunological defense of the specimens and thus could facilitate the infection in both amphibians and not in the other specimens sharing the same habitat.

The taxonomic identification of Saprolegnia is traditionally done with a detailed description of morphological characteristics, especially sexual structures as oogonia, antheridia or ornamentation present on the walls of the oogonia. We induced those characteristics by growing the fungus under specific conditions of temperature, prolonged incubation periods and specific nutrients. This classification system based on morphological features alone to identify the genus of the fungus is not fully effective in determining the species in isolates that do not produce any sexual structures typical of this fungus. Consequently, most authors suggest using molecular methods for the confirmatory identification of the fungus (22); however, it was not possible for us to do identification at the species level for the fungus Saprolegnia because specimens studied were preserved in formalin, therefore the fungus could not grow in synthetic media. Additionally, due to the preservation of the fungus in formalin, it was not possible to carry out an identification test.

The macroscopic description of the in vivo fungus on the specimen of Atelopus mittermeieri found dead is similar to that done by Kinkelin et al. (23) in fish. Authors report white aerial mycelium, which is a characteristic manifestation of this disease and the pathogenic fungus Saprolegnia. Similar signs were found in the specimens assessed.

Most recent attention to pathogen-driven amphibian decline has been focused on the study of chytridiomycosis as one of the fundamental causes of the decline of amphibians in Colombia and elsewhere (2, 24). In contrast, there are few reports of the presence of other microorganisms that may be involved individually or collectively in the decline of amphibians. Thus, our study points out the importance of research not only on a single agent, but also on the presence of bacteria, fungi and viruses not reported before as pathogenic microorganisms and that might be involved in the drastic decline of some amphibian populations.


Infectious diseases related to the introduction of alien species into natural habitats may be a fundamental cause contributing to the increase of emerging diseases.

Fungi of the genus Saprolegnia cause superficial fungal infections in amphibians, and represent a probable cause of decline of amphibians in Colombia in combination to chytrid fungus.

The use of molecular tools for identification of species is of relevance to Colombia, because there are no studies determining which species of Saprolegnia parasitize fish in Colombian freshwater ecosystems setting up the possibility of vertical interspecies transmission. Therefore, it is necessary to study in more detail the isolation, culture and molecular identification of the fungus.

The identification of Saprolegnia sp. on the body of adult specimens of dead frogs is an indication of pathology, because this fungus has a saprophytic life cycle, but also provides evidence of the ability of this fungus to be an opportunistic parasite of amphibians.


We want to extend our appreciation to: Nancy Rivera and late Jorge Diaz, directors of Guanenta Alto Rio Fonce Flora and Fauna Sanctuary (SFFGARF); biologists Johann Pena, Diego Riano and Laury Gutierrez for their support and field work along the monitoring of Atelopus mittermeieri populations between 2004 and 2007; as well as a special thank to Miguel Naranjo, officer of the sanctuary who supported the development of surveys in March 2010.

Financial support

This study was carried out in the project Detection of chytridiomycosis in Colombia, funded by COLCIENCIAS with grant No. 452 of 2008.

Conflicts of interest

Authors declare that there are no conflicts of interest related to the results obtained in this investigation.


(1.) Acosta AR, Rueda JV, Velasquez AA, Sanchez S, Pena J. Descubrimiento de una nueva especie de Atelopus (Bufonidae) para Colombia: ?Una luz de esperanza o el ocaso de los sapos Arlequines? Revista de la Academia Colombiana de Ciencias Exactas Fisicas y Naturales 2006; 30: 279-190.

(2.) Ruiz A, Rueda VR. Batrachochytrium dendrobatidis and Chytridiomycosis in Anuran Amphibians of Colombia. EcoHealth 2008; 5:27-33.

(3.) Kiesecker JM, Blaustein AR Synergism between UV-B radiation and a pathogen magnifies amphibian embryo mortality in nature. Proceedings of the National Academy of Sciences 1995; 92:11049-11052.

(4.) Blaustein AR, Hokit DG, O'Hara RK, Holt RA. Pathogenic fungus contributes to amphibian losses in the Pacific Northwest. Biological Conservation 1994; 67:251-254.

(5.) Kiesecker JM, Blaustein AR, Miller CR. Transfer of a Pathogen from fish to Amphibians. Conservation Biology 2001; 15(4):1064-1070.

(6.) Roberts RJ. Micologia de los Teleosteos. Patologia de los Peces. Ediciones Mundi-Prensa: Madrid 1981; 235-247.

(7.) Stueland S, Hatai K, Skaar I. Morphological and physiological characteristics of Saprolegnia spp. strains pathogenic to Atlantic Salmon, Salmo salar L. Journal of Fish Diseases 2005; 28:445-453.

(8.) Mousavi HAE, Soltani M, Khosravi A, Mood SM, Hosseinifard M. Isolation and Characterization of Saprolegniaceae from Rainbow Trout (Oncorhynchusmykiss) Eggs in Iran. Journal of Fisheries and Aquatic Science 2009; 4(6):330-333.

(9.) Tiffney WN. The Host Range of Saprolegnia parasitica. Mycologia 1939; 31(3):310-321.

(10.) Blaustein AR, Kiesecker JM. Complexity in conservation: lessons from the global decline of amphibian populations. Ecology Letters 2002; 5: 597-608.

(11.) Blaustein AR, Romansic JM, Kiesecker JM, Hatch AC. Ultraviolet radiation, toxic chemicals and amphibian population declines. Diversity and Distributions 2003; 9:123-140.

(12.) Carey C, Alexander MA. Climate change and amphibian declines: is there a link? Diversity and Distributions 2003; 9:111-121.

(13.) Daszak P, Cunningham AA, Hyatt AD. Infectious disease and amphibian population declines. Diversity and Distributions 2003; 9:141-150.

(14.) Collins JP, Storfer. Global amphibian declines: Sorting the hypotheses. Diversity & Distributions 2003; 9:89-98.

(15.) Alvarez R. asociaciones y patologias en los peces dulceacuicolas, estuarinos y marinos de Colombia: aguas libres y controladas. Boletin Cientifico. Centro de Museos. Museo de Historia Natural 2007; 11:81-129.

(16.) Pineda H, Jaramillo JE, Hecheverri DM, Olivera M. Triploidia en trucha arcoiris (Oncorhynchus mykiss): posibilidades en Colombia. Revista Colombiana de Ciencias. Pecuarias 2004; 17(1):45-52.

(17.) Fernandez MJ, Ortiz ME, Lizana M, Dieguez J. Saprolegnia diclina: another species responsible for the emergent disease 'Saprolegnia infections' in amphibians. FEMS Microbiological Letter 2008; 279:23-29.

(18.) Romansic JM, Diez KA, Higashi EM, Johnson E, Blaustein AR. Effects of the pathogenic water mold Saprolegnia ferax on survival of amphibian larvae. Diseases of Aquatic Organisms 2009; 83(3):187-193.

(19.) Seymour RL. The Genus Saprolegnia. Nova Hedwigia 1970; 19:1-124.

(20.) Roland A, Knapp T, Kathleen R, Matthews. Non-Native Fish Introductions and the Decline of the Mountain Yellow-Legged Frog rom within Protected Areas. Conservation Biology 2000; 14:428-43822. Noga EJ. Fish disease. Iowa University Press 2000; 117-120

(21.) Hughes GC. Seasonal periodicity of the Saprolegniaceae in the Southeastern of United States. British Micology Society 1962; 45: 519-531

(22.) Hulvey JP, Padgett DE, Bailey C. Species boundaries within Saprolegnia (Saprolegniales, Oomycota) based on morphological and DNA sequence data. Mycologia 2007; 99(3):421-429

(23.) Kinkelin P, Michel PH, Phittino P. Hongos y micosis, Tratado de las enfermedades de los peces. Editorial Acribia, S.A: Zaragoza Espana 1985. 109-116.

(24.) Velasquez B, Castro F, Bolivar W, Herrera MI. Infeccion por el hongo Quitrido Batrachochytrium dendrobatidis en anuros de la Cordillera Occidental de Colombia. Herpetotropicos 2008; 4:65-70.

Luis Daniel Prada-Salcedo [1], Marcela Franco-Correa [1] *, Andres Rymel Acosta-Galvis [2]

[1] Unidad de Investigaciones Agropecuarias (UNIDIA), Departamento de Microbiologia, Facultad de Ciencias. Pontificia Universidad Javeriana, Bogota, D.C., Colombia.

[2] Profesional Independiente. Consultor.


Received: 27-07-2011; Accepted: 16-11-2011
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Title Annotation:texto en ingles
Author:Prada-Salcedo, Luis Daniel; Franco-Correa, Marcela; Acosta-Galvis, Andres Rymel
Publication:Revista Universitas Scientarum
Date:Sep 1, 2011
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