Introduction
Mexico has documented the presence of six species of felines (Villa and Cervantes 2003), all with records in the State of Oaxaca (Briones-Salas and Sánchez-Cordero, 2004; Santos-Moreno 2014; Briones-Salas et al. 2016). However, there are regions within the State where there is no documented evidence of their presence. One example regards the districts of Ocotlán de Morelos and Tlacolula, both in the region of the Valles Centrales. Ocotlán de Morelos, despite its location just 30 km south of the city of Oaxaca and with an area of 857.9 km2, is characterized by a remarkable lack of information on wild mammals. Thus, from a collection of 17,670 georeferenced and confirmed records of wild mammals of Oaxaca deposited in scientific collections, only four corresponded to the whole District. The Tlacolula District spreads across 3,324.14 km2, with records for 33 mammal species (Monroy-Garcia 2009).
This note contributes to the knowledge of the geographical range of felines in the State of Oaxaca, specifically in the region of the Valles Centrales. This is crucial, as the two species recorded, namely the onza or jaguarundi (Herpailurus yagouaroundi) and the margay (Leopardus wiedii; Álvarez-Castañeda and Gonzalez-Ruiz 2018) are listed in the Norma Oficial Mexicana 059 (SEMARNAT 2010), under the category of Threatened and Endangered species, respectively, and in Appendix II of the Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES; http://www.cites.org).
Materials and Methods
H. yagouaroundi and L. wiedii were recorded through photographs and one specimen preserved as skin and skeleton. Photographs were provided by private individuals and are deposited in the Colección de Fotocolectas Biológicas at Universidad Nacional Autónoma de México (UNAM; IBUNAM-CFB). The jaguarundi was donated by private individuals and was deposited in the Colección Nacional de Mamíferos (CNMA) at Instituto de Biología, UNAM. Besides, the VertNet (http://www.vertnet.org/index.html) and CONABIO (http://www.gob.mx/Conabio) databases were reviewed, as well as the monograph of mammals of Oaxaca (Goodwin 1969) and recent publications, in search of records of both species for the State (Briones-Salas and Sánchez-Cordero, 2004; Santos-Moreno 2014; Briones-Salas et al. 2016). The determination of the specimen and the identification of photographs were based on Hall (1981), Aranda (2012); also, identifications were supported by comparison with reference specimens deposited at CNMA, and by expert opinions.
Results
The first record corresponds to one jaguarundi found on 11 May 2013 at 18:00 hrs at “Latajo”, 3.7 km south of La Garzona (16.64° N, -96.64° W, 2,362 masl), municipality of San José del Progreso (IBUNAM-CFB-38860). The local vegetation is oak forest (Figure 1a). The second jaguarundi specimen is a female, which was found dead on 3 December 2015, 1.6 km NE to El Chacal (16.69° N, -96.12° W, 1,141 masl), municipality of San Pedro Totolapan. The local vegetation is tropical deciduous forest. The somatic measures of the specimen, in millimeters, are: total length 675; vertebral tail 295, right hind leg 114, and ear 40; its weight was 1,000 g (CNMA 47966). This species displays two color phases, red and gray (Reid 1997); both specimens recorded were gray in color. The third record corresponds to a margay male, found on 24 March 2016 at 15:00 hrs at “El Hueco de la Hiesca”, 4.7 km SSE of La Garzona (16.63° N, -96.62° W, 2,153 masl), municipality of San José del Progreso (IBUNAM-CFB-38861). The local vegetation is pine forest (Figure 1b).
Discussion and Conclusions
The jaguarundi is considered as a common species in Oaxaca (Goodwin 1969). However, only 12 individuals have been recorded on the Pacific and Gulf of Mexico slopes. The most recent records have expanded its distribution range to the northwest of the State (Briones-Salas and Sánchez-Cordero, 2004; CONABIO 2010a; Briones-Salas et al. 2016) and to the Tehuacán-Cuicatlán Biosphere Reserve (Botello et al. 2013). The record closest to those described in this work is located to the south, in San Miguel Suchixtepec (CONABIO 2010a), at 63.5 km from San José del Progreso and 76 km from San Pedro Totolapan (Figure 2).
Two subspecies of margay have been historically recorded in Oaxaca: L. wiedii oaxacensis, which inhabits the upper parts of the center of the state, and L. w. yucatanica, distributed toward the Isthmus of Tehuantepec in the arid tropical region (Goodwin 1969). Subsequent works have documented their presence to the north of the State, in temperate humid and semiwarm climates: mountain cloud forests, pine forests, and oak forests (Cinta 2007; Perez 2008; CONABIO 2010b; Cinta-Magallon et al. 2012), and in the coastal region (Meraz et al. 2010). The margay in tropical deciduous forest in Oaxaca was first recorded in the Tehuacán-Cuicatlán Biosphere Reserve (Botello et al. 2006).
Only five records belong to the center of the state of Oaxaca, located in the districts Centro (Goodwin 1969; CONABIO 2010b), Etla (CONABIO 2010b), and Mixe, where the presence of margay was recorded from footprints in a pine forest (Lavariega et al. 2012). The record closest to the one of San José del Progreso, district of Ocotlán de Morelos, is located 48 km to the north, in the municipality of Oaxaca de Juárez (Figure 2; CONABIO 2010b).
The information reported here contributes to the knowledge of the current geographical distribution of two species that are key for conservation, in two districts that have been relegated in mammal research and which now could be essential for understanding the displacement of species. These data provide baseline information for planning biological corridors, which are required given the accelerated changes of land use across large areas of Mexico in general and of the State of Oaxaca in particular, forcing wildlife individuals to search for new habitats to thrive.