|Scientific Name:||Leptonycteris yerbabuenae|
|Species Authority:||Martínez & Villa-R, 1940|
|Taxonomic Notes:||Formerly it was treated as a subspecies of L. curasoae (see Simmons, 2005). Arita and Humphrey (1988) determined that sanborni is a junior synonym of yerbabuenae and that yerbabuenae is a subspecies of L. curasoae. Koopman (in Wilson and Reeder 1993) used the name L. curasoae for the species occurring in the southwestern United States. Simmons (in Wilson and Reeder 2005) cited references supporting her listing of L. curasoae and L. yerbabuenae as distinct species; the latter species is the one occurring in the United States.
Prior to 1962 specimens of what was then known as L. sanborni were reported as L. nivalis.
|Red List Category & Criteria:||Vulnerable A2c ver 3.1|
|Assessor(s):||Arroyo-Cabrales, J., Miller, B., Reid, F., Cuarón, A.D. & de Grammont, P.C.|
|Reviewer(s):||Medellín, R. (Chiroptera Red List Authority) & Schipper, J. (Global Mammal Assessment Team)|
Listed as Vulnerable because of a population decline, estimated to be >30% over the last 10 years, inferred from over-exploitation, shrinkage in distribution, and habitat destruction and degradation.
|Range Description:||This species is known from central California (Constantine 1998), southern Arizona, and New Mexico (USA) to Honduras and El Salvador (Simmons, 2005). It occurs from lowlands to 2,600 m (usually below 1,800 m) (Reid, 1997).|
Native:El Salvador; Guatemala; Honduras; Mexico; United States
|Upper elevation limit (metres):||2600|
|Range Map:||Click here to open the map viewer and explore range.|
|Population:||It is generally uncommon (Reid, 1997). This species is represented by a large number of occurrences or subpopulations. Arita (1991) mapped well over 100 collection sites in Mexico. Arita and Humphrey (1988) reported 269 historical and currently occupied localities in Mexico. Total adult population size is unknown but exceeds 100,000. A single roost in northern Mexico supports probably more than 100,000 individuals. This species is widespread and abundant in Mexico (Arita and Prado 1999). See Cockrum and Petryszyn (1991) for historical and recent population estimates for several sites in Arizona (no decline is evident) and Sonora.
Cockrum and Petryszyn (1991) strongly disputed the reported decline of this species and, in reviewing pertinent data, concluded that little evidence exists to document a long-term decline in Arizona, New Mexico, and Sonora; these authors stated "the various recent reports of disappearance appear to be, at least in part, the result of not looking in the right places at the right times" and further reported that "current populations...are little, if any, decreased from those of a quarter century ago. It even has been suggested that populations have increased in the past century because of more suitable roosts being available as a result of mining activity in the area."
|Current Population Trend:||Decreasing|
|Habitat and Ecology:||This species occurs in thorn scrub and deciduous forest. Its range corresponds closely to the distribution of the mezcal plant (Agave angustifolia) in Mexico (Arita, 1991). This bat roosts in caves and mines, often in colonies of several thousand. It emerges about an hour after sunset to feed on nectar and pollen of agaves and saguaro cactus in Arizona. It lands on the flowers or may hover for short periods to feed. Plant species visited in central Mexico are similar to those for L. nivalis. Some fruit and insects are also taken. Night roosts, including buildings, are used after feeding (Reid, 1997). Northern population migrate south in September and return in May. Young are born in May to June in large maternity colonies (Barbour and Davis, 1969).
Extent of occurrence, area of occupancy, number of subpopulations, and population size likely are stable or declining at a rate of less than 10 percent over 10 years or three generations.
The habitat in Mexico is primarily tropical deciduous forest and thorn forest (Arita 1991). In the United States, this bat roosts in old mines and caves at the base of mountains near alluvial fans vegetated with agave, yucca, saguaro, and organ pipe cactus (Barbour and Davis 1969). Young are born in maternity colonies in caves and mines.
|Major Threat(s):||USFWS (1987, 1989) stated that the species was threatened by disturbance of roosts, loss of food sources through land clearing and human exploitation, and direct killing by humans. Overall, however, this species does not appear to be very threatened. Habitat loss, cave issues, as mining and recreation.|
|Conservation Actions:||Avoid habitat loss. In Mexico is listed as threatened under NOM - 059 - SEMARNAT - 2001. Also is listed as priority for conservation (Arroyo-Cabrales pers. comm.). USFWS list the species as endangered.|
|Citation:||Arroyo-Cabrales, J., Miller, B., Reid, F., Cuarón, A.D. & de Grammont, P.C. 2008. Leptonycteris yerbabuenae. The IUCN Red List of Threatened Species 2008: e.T136659A4324321. . Downloaded on 26 June 2016.|