Globally Threatened Amphibian Species Part 1

Globally Threatened Amphibian Species Part 1 Globally Threatened Amphibian Species Part 1

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224 Threatened Amphibians of the World CR Colostethus leopardalis Rivero, 1978 Critically Endangered A2ace; B2ab(v) Order, Family: Anura, Dendrobatidae Country Distribution: Venezuela Current Population Trend: Decreasing Geographic Range This species is known only from a very restricted area near Páramo de Mucubají, Sierra de Santo Domingo, in estado Mérida, in the Venezuelan Andes, from 2,435-3,300m asl. Population It has not been seen in at least a decade, and its range is very much reduced. Habitat and Ecology It inhabits páramo grassland and sub-páramo shrubland environments and cloud forest, the highest environments in the Venezuelan Andes, resembling alpine tundra, but with daily temperature extremes. It is usually found within grasses and frailejones (Espeletia spp.), usually along and within streams. Major Threats Introduced trout and possibly disease might be threatening this species. This species shares its habitat with Atelopus mucubajiensis, a páramo frog well known for having experienced a dramatic population decline (La Marca and Reinthaler 1994; Lotters 1996; La Marca and Lotters 1997) probably due to chytridiomycosis, and so this disease must also be suspected in C. leopardalis. Conservation Measures There is a population within Parque Nacional Sierra Nevada (Mérida State), in the Venezuelan Andes. Surveys are required to determine the population status of this species. Given the potential risk of disease, there might be a need for the establishment of a captive-breeding programme. Notes on taxonomy: We follow La Marca (1994a) in assigning this species to the genus Colosthethus, not Nephelobates. Bibliography: Barrio Amorós, C.L. (2001), Barrio Amorós, C.L. (2004), La Marca, E. (1994a), La Marca, E. and Lötters, S. (1997), La Marca, E. and Reinthaler, H.P. (1991), Lötters, S. (1996), Mijares-Urrutia, A. (1991), Péfaur, J.E. and Rivero, J.A. (2000), Rivero, J.A. (1976), Vial, J.L. and Saylor, L. (1993) Data Providers: Enrique La Marca, Juan Elías García-Pérez EN Colostethus mandelorum (Schmidt, 1932) Endangered B1ab(iii) Order, Family: Anura, Dendrobatidae Country Distribution: Venezuela Current Population Trend: Decreasing Geographic Range This species is restricted to the Cerro Turimiquire, a mountainous region shared between Monagas, Sucre, and Anzoátegui States, in eastern Venezuela. It has been recorded from 1,900-2,630m asl. Population It is a common species. Habitat and Ecology It inhabits cloud forest and sub-páramo shrubland. The eggs are laid on land and when hatched the male carries the larvae on his back to water, where they develop further. Major Threats The main threat is habitat loss due to agriculture, involving both crops and livestock, as well as road construction for telecommunications installations. Conservation Measures Its range includes a protected area for a dam project (Zona Protectora Macizo Turimiquire), but the habitat of this species is in need of much better protection. Bibliography: Barrio Amorós, C.L. (2004), Hardy, J.D. (1984), La Marca, E. (1993), La Marca, E. (1997), Péfaur, J.E. and Rivero, J.A. (2000), Rivero, J.A. (1961), Rivero, J.A. (1982b), Vial, J.L. and Saylor, L. (1993) Data Providers: Enrique La Marca, Jesús Manzanilla EN Colostethus mertensi (Cochran and Goin, 1964) Endangered B1ab(iii) Order, Family: Anura, Dendrobatidae Country Distribution: Colombia Current Population Trend: Decreasing Geographic Range This species is known from Cerro Munchique, and Quintana (near Popayan in Cauca Department), between 2,100 and 2,350m asl, in Colombia. Population It is a common species. Habitat and Ecology It occurs on the ground next to streams in cloud forests. It lays its eggs on the ground, which (when hatched), are transported on the backs of the male to temporary ponds where they develop further. It has not been recorded outside forest habitat. Major Threats The major threats are deforestation for agricultural development, the planting of illegal crops, logging, and human settlement. Conservation Measures The range of the species includes Parque Nacional Natural Munchique. Bibliography: Cochran, D.M. and Goin, C.J. (1964), Cochran, D.M. and Goin, C.J. (1970), Rivero, J.A. (1988), Ruiz-Carranza, P.M., Ardila-Robayo, M.C. and Lynch, J.D. (1996) Data Providers: John Lynch, Fernando Castro VU Colostethus murisipanensis La Marca, 1997 Vulnerable D2 Order, Family: Anura, Dendrobatidae Country Distribution: Venezuela Current Population Trend: Stable Geographic Range This species is known only from the type locality, stated to be “Murisipan-Tepui (05 53N, 62 04W)”, in the state of Bolívar, Venezuela, at 2,350m asl. Population It is known from only one specimen. Habitat and Ecology The single specimen was collected under a rock in tropical montane forest. Breeding habits are unknown, although the larvae probably develop in streams. Major Threats There are no current major threats, but fires, caused by lightning, are a potential threat. Conservation Measures Its range does not include any protected areas. There is a need for further survey work to determine the current population status of this species, and to monitor its status, given that it is known only from one site. Bibliography: Barrio Amorós, C.L. (2004), La Marca, E. (1996b), La Marca, E. (1997) Data Providers: Enrique La Marca, Celsa Señaris

Globally Threatened Amphibian Species 225 VU Colostethus olfersioides (A. Lutz, 1925) Vulnerable A2ac Order, Family: Anura, Dendrobatidae Country Distribution: Brazil Current Population Trend: Decreasing © Ivan Sazima Geographic Range This species is known from Rio de Janeiro State, northwards along the coast to Alagoas State, in south-eastern Brazil. It occurs up to about 400m asl. Population It used to be a very common species, but it has recently declined and is now absent from several localities at which it was previously common. Habitat and Ecology This diurnal species occurs in the leaf-litter of primary and secondary forest. It can also tolerate signifi cant habitat disturbance and is found in gardens and plantations. They lay their eggs in temporary pools, and after they hatch they are carried on the backs of the adults to streams where they complete their development. Major Threats Habitat loss, due to deforestation and agricultural development, is ongoing, but probably has not been severe enough to cause the declines that have been observed. Chytridiomycosis could be implicated, although the species occurs well below the elevation at which conditions are normally suitable for chytrid. Conservation Measures It is known to occur in several protected areas, such as Parque Nacional da Serra da Bocaina. Research to determine the causes of the current decline is urgently needed. Notes on taxonomy: Colostethus carioca, C. capixaba and C alagoanus are probably synonyms of this species (V. Verdade pers. comm.). Bibliography: Cochran, D.M. and Goin, C.J. (1970), Eterovick, P.C. et al. (2005), Izecksohn, E. and Carvalho-e-Silva, S.P. (2001), Lutz, B. (1954), Rivero, J.A. (1988), Verdade, V.K. (2001) Data Providers: Sergio Potsch de Carvalho-e-Silva, Vanessa Verdade VU Colostethus pulchellus (Jiménez de la Espada, 1871) Vulnerable A2ace; B1ab(i,ii,iii, iv,v) Order, Family: Anura, Dendrobatidae Country Distribution: Colombia, Ecuador Current Population Trend: Decreasing © Francisco José López-López Geographic Range This species occurs in the inter-Andean páramos of southern Colombia (in Nariño and Cauca Departments) and northern Ecuador (south to Cotapaxi Province), and on the eastern slopes of the Andes from southern Colombia south to the headwaters of the Río Pastaza in Ecuador. Its altitudinal range is 1,590-2,970m asl. Population It has disappeared from sites where it used to be abundant in Ecuador, but is still common at Cosanga in Napo Province. It remains common in Colombia. Habitat and Ecology An inhabitant of both dry and humid montane forests. It is a terrestrial species, and breeding takes place in streams. It can be found in secondary growth near streams, but not in open areas. Major Threats The major threat to this species is habitat loss as a result of agricultural development (including the planting of illegal crops), logging, and human settlement; introduction of alien predatory fi sh in streams, and pollution resulting from the spraying of illegal crops, are additional threats. There is heavy deforestation as a result of wood extraction at Cosanga, where the species survives in Ecuador. The cause of declines observed in Ecuador is not clear, but could be due to habitat loss, climate change, and/or chytridiomycosis. Conservation Measures In Ecuador, its geographic range overlaps with the Parque Nacional Sumaco Napo-Galeras, Reserva Ecológica Antisana, Parque Nacional Llanganates, and the Reserva Ecológica Cayambe-Coca. It occurs in several protected areas in Colombia. The species requires close population monitoring, especially in view of the potential risk of chytridiomycosis. Notes on taxonomy: The populations from the Carchi basin might represent a distinct species (Coloma 1995). Bibliography: Coloma, L.A. (1995), Jiménez de la Espada, M. (1875), Ruiz-Carranza, P.M., Ardila-Robayo, M.C. and Lynch, J.D. (1996) Data Providers: Wilmar Bolívar, Luis A. Coloma, Santiago Ron EN Colostethus ranoides (Boulenger, 1918) Endangered B1ab(i,ii,iii,iv,v)+2ab(i,ii,iii,iv,v) Order, Family: Anura, Dendrobatidae Country Distribution: Colombia Current Population Trend: Decreasing Geographic Range This species occurs north of Villavicencio, in the eastern foothills of the Andes, Meta Department, Colombia, at 450-800m asl. Population It is rare, and was last seen in 2001, despite recent survey work in its range. Habitat and Ecology It is a terrestrial, diurnal species that occurs in foothill forest and lays its eggs in leaf-litter. The males probably take care of the eggs, and then move the larvae to small streams for their continued development. Major Threats Habitat loss caused by agricultural expansion is the main threat to this species, and oil extraction may pose a future threat. It is also threatened by the introduced bullfrog, Rana catesbeiana. Conservation Measures Although it occurs in several small private reserves, ex situ populations should be established because the entire range of this species is nearly entirely deforested and introduced bullfrogs could eliminate the species from remaining forest fragments. Further research and survey work is required to better understand its current population status and in order to advance appropriate conservation measures for this species. Notes on taxonomy: This species was removed from the synonymy of Colostethus brunneus by Silverstone (1971). Bibliography: Rivero, J.A. (1988), Rivero, J.A. and Serna, M.A. (1988), Ruiz-Carranza, P.M., Ardila-Robayo, M.C. and Lynch, J.D. (1996), Silverstone, P.A. (1971) Data Providers: Andrés Acosta-Galvis, Jose Vicente Rueda, Fernando Castro CR Colostethus ruizi Lynch, 1982 Critically Endangered B1ab(iii,v)+2ab(iii,v) Order, Family: Anura, Dendrobatidae Country Distribution: Colombia Current Population Trend: Decreasing Geographic Range This species is known from Fusagasuga, between Alto de San Miguel and Aguadita, on the western flank of the eastern Andes, Cundinamarca Department, Colombia, between 2,410 and 2,469m asl. Population It is rare, and is known from only six individuals. Its range has been completely deforested, except for one private tract of land 11ha in size. Four expeditions since 1995 have failed to turn up any individuals of this species. Habitat and Ecology It lives on the forest floor and along streams in cloud forest; it is not found outside old-growth forest. Its breeding habits are not documented, but it is assumed that breeding and larval development take place in streams. Major Threats Deforestation for the planting of crops and cattle grazing is the primary threat to this species. Conservation Measures The species is not known to occur in any protected areas. Surveys are urgently needed to determine whether or not this species still persists in the wild. Bibliography: Lynch, J.D. (1982b), Rivero, J.A. (1988), Ruiz-Carranza, P.M., Ardila-Robayo, M.C. and Lynch, J.D. (1996) Data Providers: Wilmar Bolívar, Jose Vicente Rueda

224<br />

<strong>Threatened</strong> <strong>Amphibian</strong>s of the World<br />

CR Colostethus leopardalis Rivero, 1978<br />

Critically Endangered A2ace; B2ab(v)<br />

Order, Family: Anura, Dendrobatidae<br />

Country Distribution: Venezuela<br />

Current Population Trend: Decreasing<br />

Geographic Range This species is known only from a very restricted<br />

area near Páramo de Mucubají, Sierra de Santo Domingo, in estado<br />

Mérida, in the Venezuelan Andes, from 2,435-3,300m asl.<br />

Population It has not been seen in at least a decade, and its range<br />

is very much reduced.<br />

Habitat and Ecology It inhabits páramo grassland and sub-páramo<br />

shrubland environments and cloud forest, the highest environments<br />

in the Venezuelan Andes, resembling alpine tundra, but with daily<br />

temperature extremes. It is usually found within grasses and frailejones<br />

(Espeletia spp.), usually along and within streams.<br />

Major Threats Introduced trout and possibly disease might be<br />

threatening this species. This species shares its habitat with Atelopus<br />

mucubajiensis, a páramo frog well known for having experienced a<br />

dramatic population decline (La Marca and Reinthaler 1994; Lotters<br />

1996; La Marca and Lotters 1997) probably due to chytridiomycosis,<br />

and so this disease must also be suspected in C. leopardalis.<br />

Conservation Measures There is a population within Parque Nacional Sierra Nevada (Mérida State), in the Venezuelan<br />

Andes. Surveys are required to determine the population status of this species. Given the potential risk of<br />

disease, there might be a need for the establishment of a captive-breeding programme.<br />

Notes on taxonomy: We follow La Marca (1994a) in assigning this species to the genus Colosthethus, not Nephelobates.<br />

Bibliography: Barrio Amorós, C.L. (2001), Barrio Amorós, C.L. (2004), La Marca, E. (1994a), La Marca, E. and Lötters, S. (1997), La<br />

Marca, E. and Reinthaler, H.P. (1991), Lötters, S. (1996), Mijares-Urrutia, A. (1991), Péfaur, J.E. and Rivero, J.A. (2000), Rivero, J.A.<br />

(1976), Vial, J.L. and Saylor, L. (1993)<br />

Data Providers: Enrique La Marca, Juan Elías García-Pérez<br />

EN Colostethus mandelorum (Schmidt, 1932)<br />

Endangered B1ab(iii)<br />

Order, Family: Anura, Dendrobatidae<br />

Country Distribution: Venezuela<br />

Current Population Trend: Decreasing<br />

Geographic Range This species is restricted to the Cerro<br />

Turimiquire, a mountainous region shared between Monagas, Sucre,<br />

and Anzoátegui States, in eastern Venezuela. It has been recorded<br />

from 1,900-2,630m asl.<br />

Population It is a common species.<br />

Habitat and Ecology It inhabits cloud forest and sub-páramo shrubland.<br />

The eggs are laid on land and when hatched the male carries<br />

the larvae on his back to water, where they develop further.<br />

Major Threats The main threat is habitat loss due to agriculture,<br />

involving both crops and livestock, as well as road construction for<br />

telecommunications installations.<br />

Conservation Measures Its range includes a protected area for<br />

a dam project (Zona Protectora Macizo Turimiquire), but the habitat<br />

of this species is in need of much better protection.<br />

Bibliography: Barrio Amorós, C.L. (2004), Hardy, J.D. (1984), La Marca, E. (1993), La Marca, E. (1997), Péfaur, J.E. and Rivero, J.A. (2000),<br />

Rivero, J.A. (1961), Rivero, J.A. (1982b), Vial, J.L. and Saylor, L. (1993)<br />

Data Providers: Enrique La Marca, Jesús Manzanilla<br />

EN Colostethus mertensi (Cochran and Goin, 1964)<br />

Endangered B1ab(iii)<br />

Order, Family: Anura, Dendrobatidae<br />

Country Distribution: Colombia<br />

Current Population Trend: Decreasing<br />

Geographic Range This species is known from Cerro Munchique,<br />

and Quintana (near Popayan in Cauca Department), between 2,100<br />

and 2,350m asl, in Colombia.<br />

Population It is a common species.<br />

Habitat and Ecology It occurs on the ground next to streams in cloud<br />

forests. It lays its eggs on the ground, which (when hatched), are<br />

transported on the backs of the male to temporary ponds where they<br />

develop further. It has not been recorded outside forest habitat.<br />

Major Threats The major threats are deforestation for agricultural<br />

development, the planting of illegal crops, logging, and human<br />

settlement.<br />

Conservation Measures The range of the species includes Parque<br />

Nacional Natural Munchique.<br />

Bibliography: Cochran, D.M. and Goin, C.J. (1964), Cochran, D.M. and Goin, C.J. (1970), Rivero, J.A. (1988), Ruiz-Carranza, P.M.,<br />

Ardila-Robayo, M.C. and Lynch, J.D. (1996)<br />

Data Providers: John Lynch, Fernando Castro<br />

VU Colostethus murisipanensis La Marca, 1997<br />

Vulnerable D2<br />

Order, Family: Anura, Dendrobatidae<br />

Country Distribution: Venezuela<br />

Current Population Trend: Stable<br />

Geographic Range This species is known only from the type locality,<br />

stated to be “Murisipan-Tepui (05 53N, 62 04W)”, in the state of<br />

Bolívar, Venezuela, at 2,350m asl.<br />

Population It is known from only one specimen.<br />

Habitat and Ecology The single specimen was collected under<br />

a rock in tropical montane forest. Breeding habits are unknown,<br />

although the larvae probably develop in streams.<br />

Major Threats There are no current major threats, but fires, caused<br />

by lightning, are a potential threat.<br />

Conservation Measures Its range does not include any protected<br />

areas. There is a need for further survey work to determine the<br />

current population status of this species, and to monitor its status,<br />

given that it is known only from one site.<br />

Bibliography: Barrio Amorós, C.L. (2004), La Marca, E. (1996b), La Marca,<br />

E. (1997)<br />

Data Providers: Enrique La Marca, Celsa Señaris

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