- Bolitoglossa la
( Campbell, Smith, Streicher, Acevedo & Brodie, 2010 )

 

 

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Subspecies: Unknown
Est. World Population:

CITES Status: NOT LISTED
IUCN Status: Endangered
U.S. ESA Status: NOT LISTED

Body Length:
Tail Length:
Shoulder Height:
Weight:

Top Speed:
Jumping Ability: (Horizontal)

Life Span: in the Wild
Life Span: in Captivity

Sexual Maturity: (Females)
Sexual Maturity: (Males)
Litter Size:
Gestation Period:

Habitat:

This species occurs in montane pine-oak forests (Campbell et al. 2010). In Chichicastenango, it has been found most frequently in bromeliads up to heights of 6–7 m above the ground (Campbell et al. 2010). Individuals collected near Santa Rosa Chucuyub were encountered inside or beneath rotting logs following rainy periods (Campbell et al. 2010). Immediately following disturbance to its habitat, the species can still be found provided there are still areas of refuge available; however, several years after such disturbance events the species cannot be found and therefore it is not thought to be tolerant to disturbance in the longer term (J. Campbell pers. comm. August 2019). It presumably lays eggs that undergo direct development.


Range:
This species is known from the northern edge of the Guatemalan Plateau and the extreme western portion of the Sierra de Chuacús, Guatemala (Campbell et al. 2010, S. Rovito and C. Vásquez-Almazán pers. comm. August 2019). It is likely to occur slightly more widely in the vicinity of known sites within suitable habitat (J. Campbell pers. comm. August 2019). Its elevational range is 2,100-2,430 m asl (Campbell et al. 2010) and its estimated extent of occurrence (EOO) is 422 km2, which represents 3-5 threat defined locations.

Conservation:
Conservation Actions In-Place
It has not been recorded from any protected areas.

Conservation Needed
Expansion of effective forest preservation and continued management of existing protected areas is essential for the conservation of this species. Community education and awareness programmes aimed to minimise persecution of salamanders in Guatemala are recommended. Proactive, precautionary steps should be taken to detect the arrival of Bsal in Guatemala and to establish a baseline by including the swabbing of salamanders encountered during routine amphibian monitoring activities in the country (Guatemala Red List Assessment Workshop August 2019).

Research Needed
More information is needed on this species' population status, life history and threats.

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