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Taxon ID: 44,767 Total records: 39,143

Platymantis subterrestris

Country

Country Philippines
Continent Ocean Asia

Classification

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

Taxonomy

Genus Platymantis Reference
SubGenus Vernacular Name
Species subterrestris IUCN Threat Status-Year Endangered, 2018
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 (Taylor, 1922) Country Distribution Philippines
Citation IUCN SSC Amphibian Specialist Group 2018. Platymantis subterrestris. The IUCN Red List of Threatened Species 2018: e.T17558A58474743. http://dx.doi.org/10.2305/IUCN.UK.2018-2.RLTS.T17558A58474743.en. Downloaded on 14 May 2019. Description Geographic Range NATIVE Extant (resident) Philippines NUMBER OF LOCATIONS 1-4 UPPER ELEVATION LIMIT 2,200 metres LOWER ELEVATION LIMIT 1,700 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) 4235.15 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 found in a few localities of the central cordilleras, on northern Luzon Island in the Philippines, between 1,700–2,200 m asl (A. Diesmos pers. comm. March 2018). It might also occur on Mount Polis and Mount Pulog, and may be found more widely within the central cordilleras on Luzon than currently mapped (A. Diesmos pers. comm. March 2018). The extent of occurrence (EOO) of its current known range is 4,235 km2 and it is thought to occur in fewer than five threat-defined locations. Population CURRENT POPULATION TREND Decreasing NUMBER OF MATURE INDIVIDUALS POPULATION SEVERELY FRAGMENTED No 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 It is quite rare at type locality (Mount Data), but in other sites with good forest cover it can be common (A. Diesmos pers. comm. March 2018). The number of mature frogs likely to occur at the type locality (Mount Data) falls within the range of 100–300 individuals. However, it has been found in other localities away from Mount Data, and so the total population of the species is not as small as was once thought. Due to ongoing decline in the extent and quality of habitat, the population is suspected to be decreasing. 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 inhabits arboreal microhabitats in mossy and montane rainforests. It breeds by direct development, presumably in shrub layer vegetation. It does not tolerate habitat disturbance (A. Diesmos pers. comm. March 2018). CLASSIFICATION SCHEME Habitats Suitability Major importance 1. Forest 1.9. Forest - Subtropical/Tropical Moist Montane Suitable Yes Threats Residential & commercial development Housing & urban areas Commercial & industrial areas Agriculture & aquaculture Annual & perennial non-timber crops Energy production & mining Mining & quarrying Biological resource use Logging & wood harvesting Pollution Agricultural & forestry effluents Threats in detail THREATS The most important threat to this species is the continued loss of montane forests in the cordilleras due to conversion of habitat to vegetable farms, quarrying, mining of mineral resources, and real estate development. Pollution from agricultural pesticides, which are intensively used to maintain vegetable farms, is likely to be a major factor in the loss of some subpopulations of this species from the remaining montane forests at the type locality. CLASSIFICATION SCHEME Threats Timing Stresses Scope Severity Impact score Invasive species Virus 1. Residential & commercial development 1.1. Housing & urban areas Ongoing 1. Ecosystem stresses 1.1. Ecosystem conversion 1.2. Ecosystem degradation Low Impact: 3 1.2. Commercial & industrial areas Ongoing 1. Ecosystem stresses 1.1. Ecosystem conversion 1.2. Ecosystem degradation Low Impact: 3 2. Agriculture & aquaculture 2.1. Annual & perennial non-timber crops 2.1.1. Shifting agriculture Ongoing 1. Ecosystem stresses 1.1. Ecosystem conversion 1.2. Ecosystem degradation Low Impact: 3 2.1.2. Small-holder farming Ongoing 1. Ecosystem stresses 1.1. Ecosystem conversion 1.2. Ecosystem degradation Low Impact: 3 3. Energy production & mining 3.2. Mining & quarrying Ongoing 1. Ecosystem stresses 1.1. Ecosystem conversion 1.2. Ecosystem degradation Low Impact: 3 5. Biological resource use 5.3. Logging & wood harvesting 5.3.3. Unintentional effects: (subsistence/small scale) [harvest] Ongoing 1. Ecosystem stresses 1.1. Ecosystem conversion 1.2. Ecosystem degradation Low Impact: 3 9. Pollution 9.3. Agricultural & forestry effluents 9.3.3. Herbicides and pesticides Ongoing 1. Ecosystem stresses 1.2. Ecosystem degradation 2. Species Stresses 2.1. Species mortality
Source

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Additional Info

Synonyms


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Cornufer subterrestris Taylor, 1922
Common Names


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Localities


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Species Record Updated By: Carlos Aurelio Callangan