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Overview

Brief Summary

Biology

Very little is known of the natural history of this species (2). It is active in the day, and breeding is confined to a short space of time between April and June during the rainy season (2). Huge numbers of golden toads once gathered at temporary pools of water, and as the males outnumbered females by 8:1, competition for females was fierce. Once a male forms a bond with a female, the pair are said to be in 'amplexus'; the male clasps the female tightly with his forearms around her back until they mate. During this time the male may face harassment from non-paired males trying to gain access to the female (2). Females produce 200 to 400 eggs, after hatching the larvae remain in the pool for about five weeks before metamorphosis into the terrestrial form occurs. It is thought that this toad feeds on small invertebrates, and may live underground at certain times of the year (2).
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Comprehensive Description

Description

The golden toad has not been seen since 1989, and is believed to be extinct (1). This toad displays extreme sexual dimorphism; males are a brilliant orange colour but females are dark and mottled with yellow-edged red blotches. Females also tend to be slightly larger than males. In juveniles, however, the sexes cannot be determined as they are very similar (2).
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Description

The Golden Toad is notable in its genus for being both sexually dichromatic and visually striking (Savage 1966). Male coloration is characteristically bright orange, uniform on the dorsum but sometimes slightly mottled on the venter. Female dorsal pigmentation ranges from greenish-yellow to black and is marked with bright scarlet spots edged in yellow, while the ventral surface is greenish-yellow to flesh colored. Adult female standard length ranges from 47 to 54 mm, while males range from 41 to 48 mm. Other size-based sexually dimorphic traits include a longer, more acute snout in males, and proportionally longer limbs. In both sexes, body surface is relatively smooth with the warts being granular and tipped with small black spines. Supraorbital, postorbital, canthal, and supratympanic external crests are present, which are low and warty. The tympanum is absent, and no vocal sac or slits are present. The iris is black and marked with gold flecks, and set in a horizontally elliptical pupil. Tubercles are not present on the hands and feet, and only the toes are webbed near their base.
 
See photos and film clip of Bufo periglenes at the ARKive site: http://www.arkive.org.uk/species/display.asp?id=17

A Spanish-language species account can be found at the website of Instituto Nacional de Biodiversidad (INBio).

  • Holdridge, L. R. (1967). Life Zone Ecology. Tropical Science Center, San Jose, Costa Rica.
  • Pounds, J. A., Fogden, M. P. L., and Campbell, J. H. (1999). ''Biological response to climate change on a tropical mountain.'' Nature, 398(6728), 611-615.
  • Pounds, J. A., and Crump, M. L. (1994). ''Amphibian declines and climate disturbance: The case of the Golden Toad and the Harlequin Frog.'' Conservation Biology, 8(1), 72-85.
  • Pounds, J. A., Fogden, M. P. L., Savage, J. M., and Gorman, G. C. (1997). "Tests of null models for amphibian declines on a tropical mountain." Conservation Biology, 11(6), 1307-1322.
  • Anchukaitis, K. J., and Evans, M. N. (2010). ''Tropical cloud forest climate variability and the demise of the Monteverde golden toad .'' Proceedings of the National Academy of Sciences, online before print, http://www.pnas.org/content/early/2010/02/25/0908572107.abstract. .
  • Crump, M. L., Hensley, F. R., and Clark, K. L. (1992). ''Apparent decline of the Golden Toad: Underground or extinct?'' Copeia, 1992(2), 413-420.
  • Jacobson, S. K. and Vandenberg, J. J. (1991). ''Reproductive ecology of the endangered Golden Toad (Bufo periglenes).'' Journal of Herpetology, 25(3), 321-327.
  • Lips, K. L., Diffendorfer, J., Mendelson, J. R., III, and Sears, M. W. (2008). ''Riding the wave: Reconciling the roles of disease and climate change in amphibian declines.'' PLoS Biology, 6, e72.
  • Rohr, J. R., Raffel, T. R., Romansic, J. M., McCallum, H., and Hudson, P. J. (2008). ''Evaluating the links between climate, disease spread, and amphibian declines.'' Proceedings of the National Academy of Sciences, 105, 17436-17441.
  • Savage, J. M. (1966). ''An extraordinary new toad (Bufo) from Costa Rica.'' Revista de Biologica Tropical, 14(2), 153-167.
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Distribution

Range Description

This species was known only from the Reserva Biológica Monteverde, Costa Rica, at elevations of 1,500-1,620m asl.
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Geographic Range

The golden toad once occupied a small area of 4 km2 of elfin cloud forest on the Cordillera de Tilaran in northern Costa Rica. This area is now known as the Monteverde Cloud Forest Preserve (Pounds, 1996).

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Distribution and Habitat

The Golden Toad is found in a small area (less than 10 square kilometers) contained in the Monteverde Cloud Forest Preserve in the Cordillera de Tilaran, near Monteverde, Provincia de Puntarenas, Costa Rica. The habitat is undisturbed, elfin cloud forest, consisting of an understory of mosses, ferns, and epiphytes, and a canopy including Didymopanex pittieri, Clusia alata, Oreopanax nubigenum, and Zanthoxylum melanostichum (Jacobson and Vandenberg 1991). The area experiences a distinct dry season, dominated by tradewind-based precipitation rising from the Caribbean basin, and a wet season, characterized by convectional storms from the Pacific lowlands (Crump et al. 1992). Mean annual biotemperature ranges from 12 to 18 degrees Celsius, and rainfall annually is over 4000 mm (Savage 1966). The habitat is characterized by Holdridge (1967) as a lower-montane rain-forest lifezone.
  • Holdridge, L. R. (1967). Life Zone Ecology. Tropical Science Center, San Jose, Costa Rica.
  • Pounds, J. A., Fogden, M. P. L., and Campbell, J. H. (1999). ''Biological response to climate change on a tropical mountain.'' Nature, 398(6728), 611-615.
  • Pounds, J. A., and Crump, M. L. (1994). ''Amphibian declines and climate disturbance: The case of the Golden Toad and the Harlequin Frog.'' Conservation Biology, 8(1), 72-85.
  • Pounds, J. A., Fogden, M. P. L., Savage, J. M., and Gorman, G. C. (1997). "Tests of null models for amphibian declines on a tropical mountain." Conservation Biology, 11(6), 1307-1322.
  • Anchukaitis, K. J., and Evans, M. N. (2010). ''Tropical cloud forest climate variability and the demise of the Monteverde golden toad .'' Proceedings of the National Academy of Sciences, online before print, http://www.pnas.org/content/early/2010/02/25/0908572107.abstract. .
  • Crump, M. L., Hensley, F. R., and Clark, K. L. (1992). ''Apparent decline of the Golden Toad: Underground or extinct?'' Copeia, 1992(2), 413-420.
  • Jacobson, S. K. and Vandenberg, J. J. (1991). ''Reproductive ecology of the endangered Golden Toad (Bufo periglenes).'' Journal of Herpetology, 25(3), 321-327.
  • Lips, K. L., Diffendorfer, J., Mendelson, J. R., III, and Sears, M. W. (2008). ''Riding the wave: Reconciling the roles of disease and climate change in amphibian declines.'' PLoS Biology, 6, e72.
  • Rohr, J. R., Raffel, T. R., Romansic, J. M., McCallum, H., and Hudson, P. J. (2008). ''Evaluating the links between climate, disease spread, and amphibian declines.'' Proceedings of the National Academy of Sciences, 105, 17436-17441.
  • Savage, J. M. (1966). ''An extraordinary new toad (Bufo) from Costa Rica.'' Revista de Biologica Tropical, 14(2), 153-167.
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Historic Range:
Costa Rica

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Range

This species was known from a small area of undisturbed montane cloud forest in northern Costa Rica, Central America. This region has been designated as the Monteverde Cloud Forest Reserve (2).
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Physical Description

Morphology

Physical Description

The golden toad is an extreme example of a sexually dimorphic amphibian. The males possess a very striking orange coloration. The females are black with scarlet blotches edged in yellow. The females range in length from 42 -- 56 mm while the males are 39 -- 48 mm. The striking physical differences between male and female cannot be determined until adulthood. Juveniles tend to be unsexable since they carry similar characteristics and body size (Jacobson, 1991).

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Type Information

Paratype for Incilius periglenes
Collection: Smithsonian Institution, National Museum of Natural History, Department of Vertebrate Zoology, Division of Amphibians & Reptiles
Preparation: Ethanol
Year Collected: 1967
Locality: Monteverde, 2 mi ENE of, Alajuela, Costa Rica
Elevation (m): 1590 to 1590
  • Paratype: Savage, J. M. 1967. Revista de Biología Tropical. 14 (2): 153.
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Paratype for Incilius periglenes
Collection: Smithsonian Institution, National Museum of Natural History, Department of Vertebrate Zoology, Division of Amphibians & Reptiles
Preparation: Ethanol
Year Collected: 1967
Locality: Monteverde, 2 mi ENE of, Alajuela, Costa Rica
Elevation (m): 1590 to 1590
  • Paratype: Savage, J. M. 1967. Revista de Biología Tropical. 14 (2): 153.
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© Smithsonian Institution, National Museum of Natural History, Department of Vertebrate Zoology, Division of Amphibians & Reptiles

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Paratype for Incilius periglenes
Collection: Smithsonian Institution, National Museum of Natural History, Department of Vertebrate Zoology, Division of Amphibians & Reptiles
Preparation: Ethanol
Year Collected: 1967
Locality: Monteverde, 2 mi ENE of, Alajuela, Costa Rica
Elevation (m): 1590 to 1590
  • Paratype: Savage, J. M. 1967. Revista de Biología Tropical. 14 (2): 153.
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Ecology

Habitat

Habitat and Ecology

Habitat and Ecology
It lived in cloud and elfin forest, and was recorded breeding in temporary pools at the beginning of the rainy season.

Systems
  • Terrestrial
  • Freshwater
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Habitat

The golden toad occupies a wet, montane area of the forest in northern Costa Rica. The elevation of this habitat ranges from 2000 -- 2100 meters (Jacobson, 1991).

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Habitat

The golden toad inhabits wet montane forest at 2,000 to 2,100 metres above sea level (2).
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Trophic Strategy

Food Habits

There are little information regarding this species' food habits since they have been primarily observed during the breeding season and live very secretive lives within the forests. Judging by size, many would agree that they feed on smaller invertebrates (Jacobson, 1991).

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Life History and Behavior

Reproduction

Reproduction

The golden toad is an explosive breeder during the months of April through June in which there is a heavy rainy season. The toads gather in enormous numbers around small, temporary pools and other water-filled depressions that are located within the forest. During this time, the competition between males for females is quite fierce. The males generally outnumber the females by an 8:1 ratio. It is at this time that males will mate with almost any moving object and molest other pairs that were in amplexus. Males also exhibited a behavior known as "toad balls" in which 4-10 males would clasp each other. However, a successful mating would produce around 200 to 400 eggs. The large diameter of the eggs is around 3.0 mm (Jacobson, 1991) The larval forms are all unsexable because of the same size and color. They remain in the pool and take up to 5 weeks to metamorphose (Harding, 1993).

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Conservation

Conservation Status

IUCN Red List Assessment


Red List Category
EX
Extinct

Red List Criteria

Version
3.1

Year Assessed
2004

Assessor/s
Alan Pounds, Jay Savage, Federico Bolaños

Reviewer/s
Global Amphibian Assessment Coordinating Team (Simon Stuart, Janice Chanson, Neil Cox and Bruce Young)

Contributor/s

Justification
Listed as Extinct because it has not been recorded since 1989, and extensive searches in the appropriate habitat, during the appropriate season within the known range, have failed to locate this species.

History
  • 1996
    Critically Endangered
  • 1994
    Endangered
    (Groombridge 1994)
  • 1990
    Endangered
    (IUCN 1990)
  • 1988
    Endangered
    (IUCN Conservation Monitoring Centre 1988)
  • 1986
    Endangered
    (IUCN Conservation Monitoring Centre 1986)
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Conservation Status

Unfortunately, the golden toad is a reproductively vulnerable species. They are classified as having a "narrow window of time" in order to breed. During the rainy season, just the right amount of rain must fall in order to have a successful year. If the rains are too heavy, the larva might flow onto the forest floor and be stranded. However, if the rains are too light, the larvae will desiccate. During 1987, there was a major population crash in the golden toads. Due to erratic weather, the pools dried up before the larva had matured. Out of potential 30,000 toads, only 29 had survived. Since then, only a few scattered individuals had been found up until 1991 when no toads were reported. Finding out why this happened is a mystery. Some say that global warming caused the erratic weather that destroyed the reproductive efforts of the golden toad. Others say it was deforestation around the preserve that killed many of the adults when they left the reproductive area. Finally, some say that the toads are simply hiding out until the conditions are right to reproduce. Overall, no one can say for sure and only time will tell. Until then, their reproductive area is still protected if and when they return (Harding, 1993).

IUCN Red List of Threatened Species: extinct

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Current Listing Status Summary

Status: Endangered
Date Listed: 06/14/1976
Lead Region: Foreign (Region 10) 
Where Listed:


Population detail:

Population location: entire
Listing status: E

For most current information and documents related to the conservation status and management of Incilius periglenes, see its USFWS Species Profile

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Status

Classified as Extinct (EX) on the IUCN Red List (1), and listed on Appendix I of CITES (3).
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Population

Population
Formerly a common species, no specimen has been seen since 1989. It last bred in normal numbers in 1987, and its breeding sites were well known. In 1988, only eight males and two females could be located. In 1989, a single male was found, and was the last record of the species. Extensive searches since this time have failed to produce any more records (as of August, 2007).
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Life History, Abundance, Activity, and Special Behaviors

The Golden Toad is a fossorial species, which remains hidden underground throughout the year, emerging only for a short breeding season. During the onset of the wet season (March to June), B. periglenes breeds explosively in shallow pools or depressions (depth up to 0.1 m), particularly those formed by tree roots (Jacobson and Vandenberg 1991). They are gregarious during breeding, and because of a heavily male-biased sex ratio, females become a limiting resource. Intense male agonistic behavior has been observed, both between lone males and against pairs in amplexus (Jacobson and Vandenberg 1991). However, competition seems to manifest mainly as scramble competition for females, as attacking pairs in amplexus seemed to have little effect and no female choice seems to be operating (Jacobson and Vandenberg 1991). Females deposit two to four hundred large eggs at a time, and tadpoles require five weeks to metamorphose (Crump et al. 1992). It has been noted that a prolonged time may be taken for mating, as one pair remained in amplexus 25 hours after their initial marking (Jacobson and Vandenberg 1991).

Jacobson and Vandenberg (1991) describe two call types, one as a release call (usually in combination with body vibrations) and characterized as a low intensity trill, and another which was not linked to any physical interactions (only one male issued the call while in amplexus).

Records and personal observations of B. periglenes document its abundance from 1971 to 1987, after which it abruptly disappeared (with 1,500 individuals recorded in 1987, five individuals found in 1988 and one in 1989; Pounds and Crump 1994), and it has not been seen since (Pounds et al. 1997).

  • Holdridge, L. R. (1967). Life Zone Ecology. Tropical Science Center, San Jose, Costa Rica.
  • Pounds, J. A., Fogden, M. P. L., and Campbell, J. H. (1999). ''Biological response to climate change on a tropical mountain.'' Nature, 398(6728), 611-615.
  • Pounds, J. A., and Crump, M. L. (1994). ''Amphibian declines and climate disturbance: The case of the Golden Toad and the Harlequin Frog.'' Conservation Biology, 8(1), 72-85.
  • Pounds, J. A., Fogden, M. P. L., Savage, J. M., and Gorman, G. C. (1997). "Tests of null models for amphibian declines on a tropical mountain." Conservation Biology, 11(6), 1307-1322.
  • Anchukaitis, K. J., and Evans, M. N. (2010). ''Tropical cloud forest climate variability and the demise of the Monteverde golden toad .'' Proceedings of the National Academy of Sciences, online before print, http://www.pnas.org/content/early/2010/02/25/0908572107.abstract. .
  • Crump, M. L., Hensley, F. R., and Clark, K. L. (1992). ''Apparent decline of the Golden Toad: Underground or extinct?'' Copeia, 1992(2), 413-420.
  • Jacobson, S. K. and Vandenberg, J. J. (1991). ''Reproductive ecology of the endangered Golden Toad (Bufo periglenes).'' Journal of Herpetology, 25(3), 321-327.
  • Lips, K. L., Diffendorfer, J., Mendelson, J. R., III, and Sears, M. W. (2008). ''Riding the wave: Reconciling the roles of disease and climate change in amphibian declines.'' PLoS Biology, 6, e72.
  • Rohr, J. R., Raffel, T. R., Romansic, J. M., McCallum, H., and Hudson, P. J. (2008). ''Evaluating the links between climate, disease spread, and amphibian declines.'' Proceedings of the National Academy of Sciences, 105, 17436-17441.
  • Savage, J. M. (1966). ''An extraordinary new toad (Bufo) from Costa Rica.'' Revista de Biologica Tropical, 14(2), 153-167.
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Threats

Threats

Major Threats
Its restricted range, global warming, chytridiomycosis and airborne pollution probably contributed to this species' extinction.
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Life History, Abundance, Activity, and Special Behaviors

The disappearance of the golden toad is perhaps the most striking case of amphibian decline, not only because its habitat and dispersion ability seem to have been unaffected (Pounds et al. 1997), but also because of the abrupt nature of its decline. The documented story is a good one, beginning with Savage's (1966) preliminary description, spanning through the late 1980's when B. periglenes disappeared, and continuing now with extensive causal analysis. The history of abundance begins with Savage's (1966) initial sighting in 1964, when he noted that "within a radius of 5 meters at least 200 toads were visible." In 1977, Jacobson and Vandenberg (1991) counted 988 individuals in a single day, as compared to a greatest daily count of 85 in 1982. The last significant record came from May 1987, when Crump et al. (1992) observed a total of 1500 adult toads over the duration of the breeding season. This count was reduced to a single toad in both 1988 and 1989 (Pounds and Crump 1994), and none have been found thereafter (Pounds et al. 1997). The extremely limited geographic distribution and fragile status of B. periglenes was internationally recognized when the International Union for the Conservation of Nature (IUCN) listed it as Endangered in 1979. In 1996, the status of the Golden Toad was revised to Critically Endangered, and in 2001, the IUCN declared the Golden Toad formally Extinct.

The rapid manner in which this population vanished, from 1500 to none in just a few years, has led to the argument that B. periglenes suffered from a high adult mortality rather than the gradual effects expected from poor juvenile recruitment or unsuccessful breeding (Pounds and Crump 1994). This reasoning, in conjunction with the toad's pristine habitat, have centered causal hypotheses around abiotic factors involving climate change (Pounds et al. 1999).

Field studies reported complete egg desiccation in both 1982 (Jacobson and Vandenberg 1991) and in 1987 (Crump et al. 1992). This seems readily explainable by the warming of the pools and the low level of precipitation, which produced drier conditions overall (Pounds and Crump 1994). However, a causal explanation for the disappearance of the adult toads is not as forthright. Certain factors have been ruled out, such as the detrimental effects of Ultraviolet (UV) exposure and pH contamination. Crump et al. (1992) argue that the Golden Toad's fossorial lifestyle and the heavy cloud cover of the montane environment should prevent damaging UV radiation, while their tests of pH change in cloud water, convective and advective precipitation turned up negative. Examining weather data, Pounds and Crump (1994) noted the correlation between the desiccation events and the adult disappearance, and the 1982-1983 and the 1986-1987 El Niño/Southern Oscillation. This led them to propose several climate-based hypotheses: moisture stress, temperature stress, climate-linked epidemic hypothesis (see Pounds et al. 2006), and the climate-linked contaminant pulse hypothesis. Pounds et al. (1999) added support to the climate-induced decline in their careful analysis of precipitation, air temperature, sea surface temperature, and stream flow patterns in relation to tropical anuran, avian, and anoline lizard communities. They concluded, as did Pounds et al. (2006) that it was not simply the effect of the El Niño/Southern Oscillation, but rather a global warming trend in general (this trend remained significant with the El Niño fluctuations included) which crossed a threshold in late 1980's and precipitated a broad tropical anuran decline. This was matched by a decline in anoline lizards, and resulted in significant restructuring of tropical avian communities. However, Lips et al. (2008) reanalyzed the data of Pounds et al. (2006), and argued that the climate-linked epidemic hypothesis was not supported, as did Rohr et al. (2008). Anchukaitis and Evans (2010) reconstructed a century of climatic data for Monteverde, Costa Rica, and suggested that cloud forest ecology changes have been driven by natural variability in the local climate (in particular, extreme dry periods associated with El Niño weather patterns) rather than by anthropogenic climate forcing.

  • Holdridge, L. R. (1967). Life Zone Ecology. Tropical Science Center, San Jose, Costa Rica.
  • Pounds, J. A., Fogden, M. P. L., and Campbell, J. H. (1999). ''Biological response to climate change on a tropical mountain.'' Nature, 398(6728), 611-615.
  • Pounds, J. A., and Crump, M. L. (1994). ''Amphibian declines and climate disturbance: The case of the Golden Toad and the Harlequin Frog.'' Conservation Biology, 8(1), 72-85.
  • Pounds, J. A., Fogden, M. P. L., Savage, J. M., and Gorman, G. C. (1997). "Tests of null models for amphibian declines on a tropical mountain." Conservation Biology, 11(6), 1307-1322.
  • Anchukaitis, K. J., and Evans, M. N. (2010). ''Tropical cloud forest climate variability and the demise of the Monteverde golden toad .'' Proceedings of the National Academy of Sciences, online before print, http://www.pnas.org/content/early/2010/02/25/0908572107.abstract. .
  • Crump, M. L., Hensley, F. R., and Clark, K. L. (1992). ''Apparent decline of the Golden Toad: Underground or extinct?'' Copeia, 1992(2), 413-420.
  • Jacobson, S. K. and Vandenberg, J. J. (1991). ''Reproductive ecology of the endangered Golden Toad (Bufo periglenes).'' Journal of Herpetology, 25(3), 321-327.
  • Lips, K. L., Diffendorfer, J., Mendelson, J. R., III, and Sears, M. W. (2008). ''Riding the wave: Reconciling the roles of disease and climate change in amphibian declines.'' PLoS Biology, 6, e72.
  • Rohr, J. R., Raffel, T. R., Romansic, J. M., McCallum, H., and Hudson, P. J. (2008). ''Evaluating the links between climate, disease spread, and amphibian declines.'' Proceedings of the National Academy of Sciences, 105, 17436-17441.
  • Savage, J. M. (1966). ''An extraordinary new toad (Bufo) from Costa Rica.'' Revista de Biologica Tropical, 14(2), 153-167.
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Threats

The population of golden toads underwent a massive crash in 1987 (2). A few individuals were found up until 1989, but the species has not been seen since then (2). Twenty out of 50 species of frogs and toads (anurans) occurring within a 30 kilometres squared area in Monteverde disappeared after synchronous population crashes in 1987, and have shown no sign of recovery (4). The area is pristine and free of direct human influences (5), a number of reasons have been proposed to explain the decline, including fungal disease, and climatic changes (4) (7).
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Management

Conservation Actions

Conservation Actions
Its entire range was protected by the Reserva Biológica Monteverde.
It is listed on CITES Appendix I (as Bufo periglenes).
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Conservation

The probable extinction of the golden toad reflects the current worldwide decline in amphibian populations. The more subtle effects of human activities on the world's ecosystems such as the build-up of pollutants, the decrease in atmospheric ozone, and changing weather patterns are beginning to take their toll. Amphibians may be our first and only early warning that these effects are starting to reach catastrophic levels (6), and may be the first sign of impending ecosystem crashes (7). In 1991, the Species Survival Commission of the IUCN established the Declining Amphibian Populations Task Force (DAPTF), which later merged into the Amphibian Specialist Group, which aims to raise money and promote research into the global amphibian decline (6).
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Relevance to Humans and Ecosystems

Benefits

Economic Importance for Humans: Positive

The golden toad is most important to the scientific world. They give us the opportunity to study rare and beautiful species up close and personal. They also strengthen the scientific community's resolution to find out why amphibians are decreasing globally.

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Source: Animal Diversity Web

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Wikipedia

Golden toad

The golden toad (Bufo periglenes) was a small, shiny, bright true toad that was once abundant in a small region of high-altitude cloud-covered tropical forests, about 30 square kilometers in area, above the city of Monteverde, Costa Rica. For this reason, it is sometimes also called the Monteverde golden toad, or the Monte Verde toad. Other common English names include Alajuela toad and orange toad. They were first described in 1966 by the herpetologist Jay Savage.[2] Since May 15, 1989, not a single B. periglenes is reported to have been seen anywhere in the world, and it is classified by the IUCN as an extinct species.[3] Its sudden extinction might have been caused by chytrid fungus and extensive habitat loss.

Contents

Description

The golden toad was one of more than 500 species in the family Bufonidae — the "true toads". B. periglenes inhabited northern Costa Rica’s Monteverde Cloud Forest Preserve, distributed over an area of roughly 10 square kilometres (3.9 sq mi) at an average elevation of 1.5 kilometres (0.93 mi).[4]

Morphology

Adult males measured just barely 5 centimetres (2.0 in) long. Males have been described as being "Day-Glo golden orange",[5] and unlike most toads their skin was shiny and bright. Jay Savage was so surprised upon first seeing them that he did not believe they could be real; he is quoted as saying: "I must confess that my initial response when I saw them was one of disbelief and suspicion that someone had dipped the examples in enamel paint."[6] Exhibiting sexual dimorphism, female toads were slightly larger than the males, and looked very different. Instead of being bright orange, females were colored dark olive to black with scarlet spots encircled by yellow.

Reproduction

Very little is known about the behavior of B. periglenes;[7] however, it is believed that they lived underground,[7] as they were not seen for most of the year. In contrast, their presence in the Cloud Forest Preserve was obvious during their mating season, which lasted only a few weeks. For a few weeks in April, after the dry season ended and the forest became wetter, males would gather in large numbers near ground puddles and wait for the females. The males would fight with each other for opportunities to mate until the end of their short mating season, after which the toads retreated to their burrows.[7] Eggs were laid in seasonal water catchments in clutches, the average size of which was 228 eggs.[8] After two months, they hatched into tadpoles.[8]

Males outnumbered females, in some years by as much as ten to one, a situation that often led bachelors to attack amplectant pairs and form what Savage once described as "writhing masses of toad balls". The eggs of the golden toad, black and tan spheres, were deposited in small pools--puddles--often no more than one inch deep. Tadpoles emerged in a matter of days, but required another four or five weeks for metamorphosis. During this period, they were highly dependent on the weather; too much rain and they would be washed down the steep hillsides, too little and their puddles would dry up. Golden toads were always found at an altitude of between forty-nine hundred and fifty-six hundred feet.

In 1987, an American ecologist and herpetologist, Martha Crump, was fortunate enough to see the toad's mating rituals. In her book, In Search of the Golden Frog [sic], she described it as "one of the most incredible sights I've ever seen", and said they looked like "statues, dazzling jewels on the forest floor".[5] On April 15, 1987, Crump recorded in her field diary that she counted 133 toads mating in one "kitchen sink-sized pool"[5] that she was observing. Five days later, she witnessed the pools in the area drying, which she attributed to the effects of El Niño-Southern Oscillation, "leaving behind desiccated eggs already covered in mold".[5] The toads attempted to mate again that May. Of the 43,500 eggs that Crump found, only twenty-nine tadpoles survived the drying of the forest's ground.[5]

The David Attenborough nature documentary Life On Earth featured a gold-colored male frog or toad paired with a red-and-black female, identified only as a very rare species from Costa Rica. These individuals are shown mating and with recently laid eggs in the episode Invasion of the Land, broadcast 20 February 1979.

Conservation history

The Monteverde Cloud Forest Preserve, the golden toad's previous habitat.

Jay Savage first discovered the toads in 1966.[2] From their discovery in 1966 for about 17 years, and from April to July in 1987, over 1500 adult toads were seen.[4] Only ten[3] or eleven toads were seen in 1988,[4] including one seen by Crump, and none has been seen since May 15, 1989, when Crump last saw the same solitary male toad that she had seen the year before.[7]

In the period between discovery and disappearance, the golden toad was commonly featured on posters promoting the biodiversity of Costa Rica.[9] There is a single anecdotal report from the 1970s of a golden toad in the mountains of Guatemala near the village of Chichicastenango,[citation needed] but this sighting has not been confirmed. There is also another extinct frog sometimes compared to the golden toad found in the same forest in Costa Rica, named Holdridge's Toad.

Extinction

In the spring of 1987, an American biologist who had come to the cloud forest specifically to study the toads counted fifteen hundred of them in temporary breeding pools. That spring was unusually warm and dry and most of the pools evaporated before the tadpoles in them had time to mature. The following year, only one male was seen at what previously had been the major breeding site. Seven males and two females were seen at a second site a few miles away. The year after, on May 15, 1989, the last sighting of only one male occurred. [10] No golden toad has been seen since then. As late as 1994, five years after the last sighting, researchers still hoped that B. periglenes continued to live in underground burrows, as similar toad species have lifespans of up to twelve years.[4] By 2004 IUCN listed the species as extinct, after an evaluation involving Savage (who had first discovered them 38 years earlier). IUCN's extinction was based on the lack of sightings since 1989 and the "extensive search[ing]" that had been done since without result.[3] In August 2010 a search organised by the Amphibian Specialist Group of the International Union for Conservation of Nature set out to look for various species of frogs thought to be extinct in the wild, including the golden toad.[11]

Jennifer Neville has examined the different hypotheses explaining the extinction of the golden toad in her article "The Case of the Golden Toad: Weather Patterns Lead to Decline". Neville comes to the conclusion that Crump's El Niño hypothesis is "clearly support[ed]" by the available data.[4] IUCN gives numerous possible reasons in its description of the past threats to the species, including "[the golden toad's] restricted range, global warming, chytridiomycosis and airborne pollution".[3] Neville also mentions arguments that an increase in UV-B radiation, fungus or parasites, or lowered pH levels contributed to the Golden Toad's extirpation.[4]

A more recent study confirms the El Niño hypothesis, in which it is stated that "The new study finds that Monteverde was the driest it’s been in a hundred years following the 1986-1987 El Niño, but that those dry conditions were still within the range of normal climate variability". The new study has shown that the Chytrid Fungus has spread due to the dry conditions caused by El Niño. [12]

References

  1. ^ Alan Pounds, Jay Savage, Federico Bolaños 2008. Incilius periglenes. In: IUCN 2008. 2008 IUCN Red List of Threatened Species. <www.iucnredlist.org>. Downloaded on 3 February 2009.
  2. ^ a b Jay Savage (1966). "An extraordinary new toad from Costa Rica". Revista de Biología Tropical 14: 153–167. http://www.scielo.sa.cr/scielo.php?pid=S0034-77442002000200033&script=sci_arttext&tlng=en. 
  3. ^ a b c d Pounds & Savage (2004). Bufo periglenes. 2006. IUCN Red List of Threatened Species. IUCN 2006. www.iucnredlist.org. Retrieved on 11 May 2006. Database entry includes a range map and a brief justification of why this species is listed as extinct.
  4. ^ a b c d e f Neville, Jennifer J. "The Case of the Golden Toad: Weather Patterns Lead to Decline". North Ohio Association of Herpetologists online. URL accessed July 27, 2006.[dead link]
  5. ^ a b c d e Crump, Marty. In Search of the Golden Frog [sic] (1998) quoted in Flannery.
  6. ^ Savage, Jay quoted in Neville, Jennifer J.
  7. ^ a b c d Flannery, Tim (2005). The Weather Makers. Toronto, Ontario: HarperCollins. pp. 114–119. ISBN 0-87113-935-9. 
  8. ^ a b Jacobson, S. K., and J. J. Vandenberg. 1991. "Reproductive ecology of the endangered golden toad (Bufo periglenes)." Journal of Herpetology 25(3):321-327. Cited in Neville.
  9. ^ Phillips, K. 1994. Tracking the vanishing frogs. New York: Penguin. 244 p. cited in Neville.
  10. ^ "Big Question for 2012 - What Animals Could Go Extinct?". Discovery News. http://news.discovery.com/animals/big-question-animals-extinct-2012-111216.html#mkcpgn=twsci1. Retrieved 12/18/11. 
  11. ^ Black, Richard (2010-08-09). "Global hunt begins for 'extinct' species of frogs". BBC. http://www.bbc.co.uk/news/science-environment-10859989. Retrieved 2010-08-09. 
  12. ^ "El Niño and a Pathogen Killed Costa Rican Toad, Study Finds". http://www.earth.columbia.edu/articles/view/2646. 

Further reading

  • Frost, Darrel et al.; Grant, Taran; Faivovich, JuliÁN; Bain, Raoul H.; Haas, Alexander; Haddad, Célio F. B.; De Sá, Rafael O.; Channing, Alan et al (2006). "The Amphibian Tree of Life". Bulletin of the American Museum of Natural History 297: 364. doi:10.1206/0003-0090(2006)297[0001:TATOL]2.0.CO;2. 
  • Field Notes from a Catastrophe - Elizabeth Kolbert.
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