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| Subspecies: | Unknown |
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| 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: | |
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.
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.




