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Taxon ID: 55,079 Total records: 39,143

Theloderma ryabovi

Classification

Kingdom Animalia (COL)
Phylum Chordata (COL)
Class Amphibia (COL)
Order Anura (COL)
Family Rhacophoridae (COL)

Taxonomy

Genus Theloderma Reference
SubGenus Vernacular Name
Species ryabovi IUCN Threat Status-Year Endangered, 2015
SubSpecies Nat'l Threat Status-Year Not Evaluated, 2000
Infraspecies Reason for Change
Infraspecies Rank CITES
Taxonomic Group Amphibians Native Status Endemic
Scientific Name Author Orlov, Dutta, Ghate and Kent, 2006 Country Distribution Viet Nam
Citation IUCN SSC Amphibian Specialist Group 2017. Theloderma ryabovi. The IUCN Red List of Threatened Species 2017: e.T136002A87450322. http://dx.doi.org/10.2305/IUCN.UK.2017-2.RLTS.T136002A87450322.en. Downloaded on 08 May 2019. Description Geographic Range NATIVE Extant (resident) Viet Nam NUMBER OF LOCATIONS 2 UPPER ELEVATION LIMIT 1,210 metres LOWER ELEVATION LIMIT 1,210 metres Geographic Range in detail ESTIMATED AREA OF OCCUPANCY (AOO) (KM²) CONTINUING DECLINE IN AREA OF OCCUPANCY (AOO) EXTREME FLUCTUATIONS IN AREA OF OCCUPANCY (AOO) ESTIMATED EXTENT OF OCCURRENCE (EOO) (KM²) 2736 CONTINUING DECLINE IN EXTENT OF OCCURRENCE (EOO) EXTREME FLUCTUATIONS IN EXTENT OF OCCURRENCE (EOO) CONTINUING DECLINE IN NUMBER OF LOCATIONS EXTREME FLUCTUATIONS IN THE NUMBER OF LOCATIONS RANGE DESCRIPTION This species is currently known only from 1,210 m Asl at a single locality in Kon Tum Province, central Viet Nam (Orlov et al. 2006). This is unlikely to represent the actual limits of the species range as similar habitat and elevations to those in its known locality occur in adjacent areas including south into north-eastern Gia Lai Province. Further surveys in these areas may uncover its presence, therefore its range has been projected beyond known sites to include these areas of suitable habitat. This species EOO is 2,736 km2, which consists of two threat-defined locations. Population CURRENT POPULATION TREND Decreasing NUMBER OF MATURE INDIVIDUALS POPULATION SEVERELY FRAGMENTED CONTINUING DECLINE OF MATURE INDIVIDUALS Population in detail EXTREME FLUCTUATIONS NO. OF SUBPOPULATIONS CONTINUING DECLINE IN SUBPOPULATIONS EXTREME FLUCTUATIONS IN SUBPOPULATIONS ALL INDIVIDUALS IN ONE SUBPOPULATION NO. OF INDIVIDUALS IN LARGEST SUBPOPULATION DESCRIPTION Nothing is currently known about the size of this species population except that it is known from only three adults and a number of juvenile individuals that were detected in a single survey (Orlov et al. 2006), despite the areas surrounding its type locality having been surveyed many times (J. Rowley pers. comm. December 2015). It is unclear whether this is due to true rarity or cryptic behaviour, and further research is needed to determine the species true abundance. Deforestation continues to affect habitat in the species range (Meyfroidt and Lambin 2008, Sodhi et al. 2009, Meyfroidt et al. 2013), and is very likely causing some declines. Habitat and Ecology SYSTEM Terrestrial HABITAT TYPE Forest GENERATION LENGTH (YEARS) CONGREGATORY MOVEMENT PATTERNS Not a Migrant CONTINUING DECLINE IN AREA, EXTENT AND/OR QUALITY OF HABITAT Yes Habitat and Ecology in detail HABITAT AND ECOLOGY This species is associated with montane primary forest and has been observed in trees 4m above the ground (Orlov et al. 2006). The species is a phytotelm breeder and reproduction presumably commences prior to April, during which time three adults including at least one male as well as tadpoles and metamorphs of different stages have been observed together in a tree hole partly filled with 20 cm of water (Orlov et al. 2006). CLASSIFICATION SCHEME Habitats Suitability Major importance 1. Forest 1.9. Forest - Subtropical/Tropical Moist Montane Suitable Yes Threats Agriculture & aquaculture Annual & perennial non-timber crops Transportation & service corridors Roads & railroads Threats in detail THREATS Habitat loss and degradation due to the effects of rapidly expanding agriculture is an ongoing threat to biodiversity throughout Southeast Asia (Sodhi et al. 2009). In the Central Highlands of Viet Nam large areas of forest are converted to agricultural land to grow cash crop plantations (e.g. rubber, coffee and tea) (Meyfroidt and Lambin 2008, Meyfroidt et al. 2013). Recent satellite imagery reveals areas of land cleared for agriculture throughout parts of this species range. The construction of roads in this area has also degraded habitat (T. Nguyen pers. comm. December 2015). CLASSIFICATION SCHEME Threats Timing Stresses Scope Severity Impact score Invasive species Virus 2. Agriculture & aquaculture 2.1. Annual & perennial non-timber crops 2.1.2. Small-holder farming Ongoing 1. Ecosystem stresses 1.1. Ecosystem conversion 1.2. Ecosystem degradation 2. Species Stresses 2.2. Species disturbance Unknown Unknown Unknown 2.1.3. Agro-industry farming Ongoing 1. Ecosystem stresses 1.1. Ecosystem conversion 1.2. Ecosystem degradation 2. Species Stresses 2.1. Species mortality 2.2. Species disturbance Unknown Unknown Unknown 4. Transportation & service corridors 4.1. Roads & railroads Ongoing 1. Ecosystem stresses 1.2. Ecosystem degradation Unknown Unknown
Source

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Additional Info

Synonyms


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Common Names


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Localities


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Species Record Updated By: Carlos Aurelio Callangan