Eleutherodactylus cundalli 

Scope: Global
Language: English

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Taxonomy [top]

Kingdom Phylum Class Order Family
Animalia Chordata Amphibia Anura Eleutherodactylidae

Scientific Name: Eleutherodactylus cundalli Dunn, 1926
Common Name(s):
English Cundall's Robber Frog
Taxonomic Source(s): Frost, D.R. 2013. Amphibian Species of the World: an Online Reference. Version 5.6 (9 January 2013). Electronic Database. American Museum of Natural History, New York, USA. Available at:

Assessment Information [top]

Red List Category & Criteria: Near Threatened ver 3.1
Year Published: 2013
Date Assessed: 2011-03-22
Assessor(s): IUCN SSC Amphibian Specialist Group
Reviewer(s): Martins, M. & Cox, N.A.
Contributor(s): Hedges, B., Wilson, B.S., Holmes, I. & Koenig, S.
Facilitator/Compiler(s): Angulo, A. & Berezdivin, D.
Listed as Near Threatened given that its extent of occurrence (EOO) is estimated to be 6,293 km2, it is currently known from eight threat-defined locations but is likely to occur in more locations, possibly greater than ten, and there is continuing decline in the extent and quality of its forest habitat in Jamaica and there is a suspected decline in the number of mature individuals. The species almost qualifies for a threatened listing under criterion B1ab(iii).
Previously published Red List assessments:

Geographic Range [top]

Range Description:This species is widely distributed in western Jamaica from sea level to 635 m asl.  Its range, taken as a proxy for extent of occurrence (EOO) is estimated to be 6,293 km2.  It is known from eight threat-defined locations, but it is likely to be more widespread (I. Holmes pers. comm. December 2012), and additional surveys in less sampled areas could reveal new records.
Countries occurrence:
Additional data:
Upper elevation limit (metres):635
Range Map:Click here to open the map viewer and explore range.

Population [top]

Population:It is more abundant than many other species of Eleutherodactylus on Jamaica and is moderately common. As long as there is a good underground retreat and a closed canopy forest, it is likely to occur in suitable areas; it is not considered to have a severely fragmented population (I. Holmes pers. comm. March 2011). Although it is considered to be a common species, it is suspected to be decreasing in some sites given the effects of bauxite mining and limestone quarrying in suitable underground habitats (S. Koenig pers. comm. March 2011). It was seen in March 2011 (S. Koenig pers. comm. March 2011).
Current Population Trend:Decreasing
Additional data:
Continuing decline of mature individuals:Yes
Population severely fragmented:No

Habitat and Ecology [top]

Habitat and Ecology:It is found in association with rocks and it is closely associated with limestone karst and/or caves and requires closed-canopy moist forest. It breeds by direct development and eggs are laid on the ground. This species exhibits extensive maternal care (Diesel et al. 1995). It does not occur in open habitats, but it can tolerate moderate disturbance insofar as there is a majority closed canopy (I.  Holmes and S. Koenig pers. comms. March 2011).
Continuing decline in area, extent and/or quality of habitat:Yes

Use and Trade [top]

Use and Trade: There are no reports of this species being utilized.

Threats [top]

Major Threat(s): The main threat is habitat degradation and loss due to bauxite mining and limestone quarrying, and to a lesser degree, it is also impacted by small-holder agriculture (yam, bananas), human settlements, tourism development (especially cave eco-tourism; I. Holmes pers. comm. March 2011; S. Koenig pers. comm. March 2011), and clear-cut logging (I. Holmes pers. comm. March 2011). Bauxite mining activity is likely to increase throughout the rest of this species' range in the future (S. Koenig pers. comm. March 2011).

Conservation Actions [top]

Conservation Actions: It occurs in several forest reserves; although management has improved over the last five years, bauxite mining continues to be a major threat factor to this species (S. Koenig pers. comm. March 2011). Additional habitat protection is needed as is restoration of natural habitats impacted by mining activities. Population monitoring is needed to assess suspected population declines.

The Amphibian Ark conservation needs assessment identifies potential for ex situ research into developing husbandry protocols for more threatened species and can also be used for conservation education due to reproductive behaviour.

Citation: IUCN SSC Amphibian Specialist Group. 2013. Eleutherodactylus cundalli. The IUCN Red List of Threatened Species 2013: e.T56543A3042373. . Downloaded on 24 June 2018.
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