Ambystoma leorae (Taylor, 1943)
Leora’s Stream Salamander, Leora’s Stream Siredon, Ajolote
|Species Description: Taylor, E. H. (1943). "Herpetological novelties from Mexico." University of Kansas Science Bulletin 29, 343–361.|
© 2014 Octavio Monroy-Vilchis (1 of 1)
Ambystoma leorae has a smaller snout-vent length than other Ambystoma mole salamanders, including Ambystoma mexicanum and Ambystoma lermaense, which also reside in Mexico (Sunny et al. 2014).
Ambystoma leorae is dark brown or black, with lighter yellow or brown mottling across its back and tail. Individuals all have mottling, but exact coloration varies between darker and lighter shades (Shaffer et al. 2008). They are not sexually dimorphic in coloration (Lemos-Espinal et al. 2017).
Individually, there is mild variation in coloration with slightly lighter and darker shades of A. leorae (Shaffer et al. 2008). Males tend to have swelling in the cloacal region on both sides of the tail while females do not (Lemos-Espinal et al. 2017).
Distribution and Habitat
Country distribution from AmphibiaWeb's database: Mexico
It prefers cold freshwater streams, pools, and slow-moving streams with high oxygen content in humid, high-altitude pine forests at elevations of about 3,000 meters above sea level (Shaffer et al. 2008, Sunny et al. 2014). There is a wide variety of vegetation in the region, including pines, firs, oaks, Mexican Alders, Mexican Strawberry Trees, Manzanitas, Mexican Lupine, Pineapple Sage, Mühlenberg Grass, Old-man Bush, Toluca Bentgrass, and Fescue Grass (Lemos-Espinal et al. 2017).
Life History, Abundance, Activity, and Special Behaviors
Adults exhibit neoteny; they retain some juvenile features such as filamentous external gills. In addition, Ambystoma retain longitudinal rows of teeth as they develop from larvae to adults. This partial paedomorphosis allows adults to take advantage of the same aquatic food sources as their larvae (Reilly and Brandon 1994).
The temperature of the water in which it lives ranges between 6 - 15°C (Monroy-Vilchis et al. 2015). Adults can be found in sites with mud, sand, or mud/gravel. Some streams have a “sinuous” condition because of erosion along the banks of the stream. Crevices formed by this erosion have been noted as a common place for the salamander to lay its egg masses (Lemos-Espinal et al. 2017).
In comparison to most salamanders (including other Ambystoma), A. leorae produces a relatively low number of eggs. The egg masses range from about 6 - 9 eggs. The low number of eggs is compensated by the fact that they lay larger eggs than other mole salamanders (Sunny et al. 2014). Eggs are laid in muddy bottom streams, attached to vegetation. They have been observed laying eggs on vegetation within crevices along the banks of the streams. Observations suggest that egg-laying occurs from April to June. This is similar to other populations of Mexican Ambystoma, as this particular month range correlates with the rainy season in central Mexico (Lemos-Espinal et al. 2017).
Their diet consists of aquatic insects (Lemos-Espinal et al. 2017).
Ambystoma mexicanum are found nearby and occupy a similar niche. Extrapolating from A. mexicanum, it is likely that A. leorae has few natural predators. However, A. mexicanum is experiencing population declines due to the introduction of the two exotic fish: carp (Cyprinus carpio) and tilapia (Oreochromis niloticus) (Zambrano et al. 2010). These fish do not prey on the adult salamanders directly but compete with salamanders for food and eat their eggs.
This species is highly aquatic across all life stages. Its eggs and larvae develop in the water, and the adults do not stray far from their natal streams (Reilly and Brandon 1994). Larvae are usually only found in sites with mud bottoms and submerged aquatic vegetation/algae (Lemos-Espinal et al. 2017).
Trends and Threats
If the amphibian pathogen, Batrachochytrium salamandrivorans, were to be introduced to the Western Hemisphere, it could have drastic impacts on A. leorae (IUCN 2020).
Relation to Humans
Possible reasons for amphibian decline
General habitat alteration and loss
IUCN SSC Amphibian Specialist Group. (2020). "Ambystoma leorae." The IUCN Red List of Threatened Species 2020: e.T59061A53974072. https://dx.doi.org/10.2305/IUCN.UK.2020-2.RLTS.T59061A53974072.en. Accessed on 19 October 2022.
Lemos-Espinal, J. A., Smith, G. R., Estrella Zamora, A. B., Woolrich-Piña, G., Montoya Ayala, R. (2017). “Natural history of the critically endangered salamander Ambystoma leorae (Caudata:Ambystomatidae) from the Río Tonatzin, Mexico.” Phyllomedusa 16,1: 3-11 [link]
Monroy-Vilchis, O., Zarco-González M. M., Domínguez-Vega, H., Sunny, A. (2015). “Ambystoma leorae (Taylor, 1943). New records, natural history notes and threat status.” Herpetozoa 27(3/4),166-168 [link]
Reilly, S. M., Brandon, R. A. (1994). “Partial paedomorphosis in the Mexican stream ambystomatids and the taxonomic status of the genus Rhyacosdiredon Dunn.” Copeia 1994(3),656-662 [link]
SEMARNAT (Secretara de Medio Ambiente y Recursos Naturales). (2010). Norma Oficial Mexicana NOM-059 Ecol-2010. Protección ambiental-Especies nativas de México de flora y fauna silvestres- Categorías de reisgo y especifaciones para su inclusion, exclusion o cambio- Lista de especies en riesgo. Diario oficial (Segunda Seccion, 30-dic).
Shaffer, H.B., Parra-Olea, G., Wake, D. (2008). "Ambystoma leorae." The IUCN Red List of Threatened Species 2008: e.T59061A11877775. http://dx.doi.org/10.2305/IUCN.UK.2008.RLTS.T59061A11877775.en. Downloaded on 15 February 2018.
Sunny, A., Monroy-Vilchis, O., Fajardo, V., Aguilera-Reyes, U. (2013). “Genetic diversity and structure of an endemic and critically endangered stream river salamander (Caudata: Ambystoma leorae) in Mexico.” Conservation Genetics 15(1), 49-59. [link]
Sunny, A., Monroy-Vilchis, O., Reyna-Valencia, C., Zarco-Gonzalez, M. (2014). “Microhabitat types promote the genetic structure of a micro-endemic and critically endangered mole salamander (Ambystoma leorae) of Central Mexico.” PLoS One 9(7), e103595 [link]
Zambrano, L., Valiente, E., Vander Zanden, M.J., (2010). “Food web overlap among native axolotl (Ambystoma mexicanum) and two exotic fishes: carp (Cyprinus carpio) and tilapia (Oreochromis niloticus) in Xochimilco, Mexico City.” Biological Invasions 12(9), 3061-3069 [link]
Originally submitted by: Kimberly Mitchell, Cortnie Meier, Mailee Danao (2022-11-07)
Description by: Kimberly Mitchell, Cortnie Meier, Mailee Danao (updated 2022-11-07)
Distribution by: Kimberly Mitchell, Cortnie Meier, Mailee Danao (updated 2022-11-07)
Life history by: Kimberly Mitchell, Cortnie Meier, Mailee Danao (updated 2022-11-07)
Larva by: Kimberly Mitchell, Cortnie Meier, Mailee Danao (updated 2022-11-07)
Trends and threats by: Kimberly Mitchell, Cortnie Meier, Mailee Danao (updated 2022-11-07)
Relation to humans by: Kimberly Mitchell, Cortnie Meier, Mailee Danao (updated 2022-11-07)
Comments by: Kimberly Mitchell, Cortnie Meier, Mailee Danao (updated 2022-11-07)
Edited by: Ann T. Chang (2022-11-07)
Species Account Citation: AmphibiaWeb 2022 Ambystoma leorae: Leora’s Stream Salamander <https://amphibiaweb.org/species/3837> University of California, Berkeley, CA, USA. Accessed Mar 24, 2023.
Feedback or comments about this page.
Citation: AmphibiaWeb. 2023. <https://amphibiaweb.org> University of California, Berkeley, CA, USA. Accessed 24 Mar 2023.
AmphibiaWeb's policy on data use.