Checklist |
Corresponding author: Julio A. Lemos-Espinal ( lemos@unam.mx ) Academic editor: Johannes Penner
© 2020 Julio A. Lemos-Espinal, Geoffrey R. Smith.
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Lemos-Espinal JA, Smith GR (2020) A conservation checklist of the amphibians and reptiles of the State of Mexico, Mexico with comparisons with adjoining states. ZooKeys 953: 137-159. https://doi.org/10.3897/zookeys.953.50881
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The State of Mexico has a unique combination of geographic characteristics and topography that promotes a high biodiversity. Unfortunately, continued human population growth of the metropolitan areas of Mexico City and Toluca have degraded the environment of the State of Mexico, which threatened its wildlife. An updated checklist of the amphibians and reptiles of the State of Mexico is provided and their conservation status summarized. The State of Mexico has 49 species of amphibians and 101 species of reptiles. The majority of the amphibians (73.5%) and reptiles (70.3%) found in the State of Mexico are endemic to Mexico. Of the amphibian and reptile species in the State of Mexico, 20.1% are IUCN listed (i.e., Vulnerable, Near Threatened, or Endangered), 18.4% are placed in a protected category by SEMARNAT (excluding NL and Pr, this last category is equivalent to the LC category of IUCN), and 34.9% are categorized as high risk by the EVS. The importance of forested habitats for the protected amphibians and reptiles in the State of Mexico suggest that management of these habitats to maintain or expand them needs to be considered.
checklist, crocodilians, frogs, herpetofauna, lizards, salamanders, snakes, turtles
Although relatively small, the State of Mexico bears unique geographic characteristics that combined with its topography create conditions that promote a high level of biodiversity. Unfortunately, these same conditions along with the continued human population growth of the metropolitan area of Mexico City and the city of Toluca have created high water and air pollution levels, deforestation, habitat fragmentation, and low water availability, which threaten the wildlife of this state (
Here, we provide an updated checklist of the amphibians and reptiles documented in the State of Mexico. We also summarize the conservation status of these species with the goal of determining if there are particular taxa of conservative concern in the State of Mexico. In addition, we consider the overlap in species between the State of Mexico and its neighboring states.
The State of Mexico is the most populous, as well as the most densely populated state in Mexico. It is located in south-central Mexico, in the highest part of the Mexican Altiplano, between 18°22'0.84"N and 20°17'9.24"N, and 100°36'46.8"W and 98°35'48.84"W (Fig.
The topography of the state is highly variable, with the highest mountains in the extreme eastern part of the state along the border with Puebla (Popocatépetl 5,380 m altitude, Iztaccíhuatl 5,203 m, Monte Tláloc 4,120 m), and in the central part of the state (Nevado de Toluca 4,643 m), as well as rugged intermontane valleys, hills and plains, with altitudes ranging from 300 m near the border with Guerrero to 5,380 m on the top of the Popocatépetl Volcano (Fig.
The State of Mexico has a variety of vegetation types (Fig.
Given the geographical location and diversity of the natural regions in the state, there are several climates in the State of Mexico (Fig.
We compiled our list of amphibians and reptiles of the State of Mexico from our field work over several years, especially within the past 5–10 years, a thorough examination of available literature on amphibians and reptiles in the state, amphibian and reptile records for the State of Mexico in VertNet.org, and amphibian and reptile records for the State of Mexico in Servicio de Descarga de Ejemplares del Sistema Nacional de Información sobre Biodiversidad (SNIB-CONABIO), data bases Amphibians State of Mexico and Reptiles State of Mexico. Amphibian names follow
We made species accumulation curves for the total herpetofauna, and amphibians and reptiles separately using the year of the first recorded observation for each species. These curves can estimate the potential species richness of amphibians and reptiles (see
The State of Mexico is home to 150 species of amphibians and reptiles representing 31 families (two introduced: Gekkonidae and Typhlopidae) and 65 genera (two introduced: Hemidactylus and Indotyphlops) (Table
The species accumulation curves for the total herpetofauna, reptiles, and amphibians all show a steep increase in the number of species documented in the State of Mexico in the second half of the 20th century, and that trend appears to be continuing, albeit at a somewhat slower rate in the 21st century (Fig.
Thirty-six of the 49 species of amphibians found in the State of Mexico are endemic to Mexico, four of them to the State of Mexico (Ambystoma bombypellum, A. granulosum, A. lermaense, and Pseudoeurycea robertsi); twelve are species found mainly along the Eje Neovolcánico of central Mexico; seven are species typical of the Pacific Coast, including the Balsas Depression; three are species characteristics of the Mexican Plateau; seven more are species with a widely distributional patterns in the Mexican Plateau, the Sierra Madre Occidental, Sierra Madre Oriental, Sierra Madre del Sur, and Eje Neovolcánico; and the remaining three are represented by scattered populations in the Mexican Plateau, Sierras Madres, and Eje Neovolcánico (Table
Amphibians and reptiles of the State of Mexico with distributional and conservation status. Vegetation Type: (1 = Oak Forest; 2 = Pine-oak Forest; 3 = Pine Forest; 4 = Tropical Deciduous Forest; 5 = Grassland; 6 = Scrubland); IUCN Status: (DD = Data Deficient; LC = Least Concern, VU = Vulnerable, NT = Near Threatened; EN = Endangered; CR = Critically Endangered; NE = not Evaluated) according to the IUCN Red List (
Vegetation type | IUCN status | SEMARNAT | EVS | Global distribution | Year of first record | Source | |
---|---|---|---|---|---|---|---|
CLASS AMPHIBIA | |||||||
ORDER ANURA | |||||||
FAMILY BUFONIDAE (5) | |||||||
Anaxyrus compactilis (Wiegmann, 1833) | 1,2,5,6 | LC | NL | H (14) | 1 | 1888 | |
Incilius marmoreus (Wiegmann, 1833) | 4 | LC | NL | M (13) | 1 | 1930 |
|
Incilius occidentalis (Camerano, 1879) | 1,2,3,6 | LC | NL | M (11) | 1 | 1941 |
|
Incilius perplexus (Taylor, 1943) | 4 | EN | NL | M (11) | 1 | 1983 |
|
Rhinella horribilis (Wiegmann, 1833) | 4 | LC | NL | L (3) | 4 | 1941 |
|
FAMILY CRAUGASTORIDAE (4) | |||||||
Craugastor augusti (Dugès, 1879) | 2,6 | LC | NL | L (8) | 2 | 1942 | Taylor 1942 |
Craugastor hobartsmithi (Taylor, 1937) | 2 | EN | NL | H (15) | 1 | 1936 |
|
Craugastor pygmaeus (Taylor, 1937) | 1,2,3 | VU | NL | L (9) | 3 | 1992 |
|
Craugastor rugulosus (Cope, 1870) | 3 | LC | NL | M (13) | 3 | 1968 |
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FAMILY ELEUTHERODACTYLIDAE (4) | |||||||
Eleutherodactylus angustidigitorum (Taylor, 1940) | 1,2,3,6 | VU | Pr | H (17) | 1 | 1954 |
|
Eleutherodactylus maurus Hedges, 1989 | 1,2,3 | DD | Pr | H (17) | 1 | 1954 |
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Eleutherodactylus nitidus (Peters, 1870) | 1,2,3 | LC | NL | M(12) | 1 | 1951 |
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Eleutherodactylus pipilans (Taylor, 1940) | 4 | LC | NL | M (11) | 3 | 1979 |
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FAMILY HYLIDAE (9) | |||||||
Dryophytes arenicolor (Cope, 1886) | 1,2,3,4,5,6 | LC | NL | L (7) | 2 | 1921 |
|
Dryophytes eximius (Baird, 1854) | 1,2,3,6 | LC | NL | M (10) | 1 | 1919 |
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Dryophytes plicatus (Brocchi, 1877) | 1,2,3,6 | LC | A | M (11) | 1 | 1912 |
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Exerodonta smaragdina (Taylor, 1940) | 4 | LC | Pr | M (12) | 1 | 1992 |
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Sarcohyla bistincta (Cope, 1877) | 1,2,3 | LC | Pr | L (9) | 1 | 1938 |
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Sarcohyla pentheter (Adler, 1965) | 4 | EN | NL | M (13) | 1 | 2009 |
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Smilisca baudinii (Duméril & Bibron, 1841) | 1,2,4,6 | LC | NL | L (3) | 4 | 1982 |
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Smilisca fodiens (Boulenger, 1882) | 4 | LC | NL | L (8) | 2 | 1968 |
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Tlalocohyla smithii (Boulenger, 1902) | 4 | LC | NL | M (11) | 1 | 1968 |
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FAMILY LEPTODACTYLIDAE (1) | |||||||
Leptodactylus melanonotus (Hallowell, 1861) | 4 | LC | NL | L (6) | 3 | 1965 |
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FAMILY MICROHYLIDAE (1) | |||||||
Hypopachus variolosus (Cope, 1866) | 4 | LC | NL | L (4) | 4 | 1941 |
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FAMILY PHYLLOMEDUSIDAE (1) | |||||||
Agalychnis dacnicolor (Cope, 1864) | 4 | LC | NL | M (13) | 1 | 1983 |
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FAMILY RANIDAE (7) | |||||||
Rana catesbeiana Shaw, 1802 | IN | IN | IN | IN | IN | 1982 |
|
Rana forreri Boulenger, 1883 | 4 | LC | Pr | L (3) | 3 | 1940 |
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Rana montezumae Baird, 1854 | 1,2,3,5,6 | LC | Pr | M (13) | 1 | 1888 |
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Rana neovolcanica Hillis & Frost, 1985 | 1,2,3 | NT | A | M (13) | 1 | 2009 |
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Rana spectabilis Hillis & Frost, 1985 | 1,2,3,5,6 | LC | NL | M (12) | 1 | 1936 |
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Rana tlaloci Hillis & Frost, 1985 | 1,2,5,6 | CR | P | H (15) | 1 | 1979 |
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Rana zweifeli Hillis, Frost & Webb, 1984 | 1,2,3,4,5 | LC | NL | M (11) | 1 | 1982 |
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FAMILY SCAPHIOPODIDAE (1) | |||||||
Spea multiplicata (Cope, 1863) | 1,5 | LC | NL | L (3) | 2 | 1940 |
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ORDER CAUDATA | |||||||
FAMILY AMBYSTOMATIDAE (8) | |||||||
Ambystoma altamirani Dugès, 1895 | 1,2,3,5 | EN | A | M (13) | 1 | 1895 |
|
Ambystoma bombypellum Taylor, 1940 | 2,5 | CR | Pr | H (15) | 0 | 1940 |
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Ambystoma granulosum Taylor, 1944 | 1,2,3,5 | CR | Pr | H (14) | 0 | 1944 |
|
Ambystoma leorae (Taylor, 1943) | 2,3,5 | CR | A | H (15) | 1 | 1943 |
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Ambystoma lermaense (Taylor, 1940) | 5 | EN | Pr | H (15) | 0 | 1940 |
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Ambystoma ordinarium Taylor, 1940 | ? | EN | Pr | M (13) | 1 | 22004 |
|
Ambystoma rivulare (Taylor, 1940) | 1,2,3,5 | DD | A | M (13) | 1 | 1940 |
|
Ambystoma velasci Duges, 1888 | 1,2,3,5,6 | LC | Pr | M (10) | 1 | 1888 |
|
FAMILY PLETHODONTIDAE (8) | |||||||
Aquiloeurycea cephalica (Cope, 1865) | 1,2,3,5 | NT | A | H (14) | 1 | 1938 |
|
Chiropterotriton orculus (cope, 1865) | 1,2,3,5 | VU | NL | H (18) | 1 | 1951 |
|
Isthmura belli (Gray, 1850) | 1,2,3,5 | VU | A | M (12) | 1 | 1938 |
|
Pseudoeurycea altamontana (Taylor, 1939) | 1,2,3,5 | EN | Pr | H (17) | 1 | 1956 |
|
Pseudoeurycea leprosa (Cope, 1869) | 1,2,3,5 | LC | A | H (16) | 1 | 1921 |
|
Pseudoeurycea longicauda Lynch, Wake, & Yang, 1983 | 1,2,3,5 | EN | Pr | H (17) | 1 | 1983 |
|
Pseudoeurycea robertsi (Taylor, 1939) | 1,2,3,5 | CR | A | H (18) | 1 | 1939 |
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Pseudoeurycea tlilicxitl Lara-Góngora, 2003 | 1,2,3,5 | EN | NL | H (17) | 1 | 2003 |
|
CLASS REPTILIA | |||||||
SUBORDER LACERTILIA | |||||||
FAMILY ANGUIDAE (5) | |||||||
Abronia deppii (Wiegmann, 1828) | 2 | EN | A | H (16) | 1 | 1979 |
|
Barisia herrerae Zaldivar-Riverón & Nieto Montes de Oca, 2002 | 2,3 | EN | NL | H (15) | 0 | 2002 | Zaldivar-Riverón and Nieto Montes de Oca 2002 |
Barisia imbricata (Wiegmann, 1828) | 1,2,3,5,6 | LC | Pr | H (14) | 1 | 1888 |
|
Barisia rudicollis (Wiegmann, 1828) | 1,2,3,5 | EN | P | H (15) | 1 | 1828 |
|
Gerrhonotus liocephalus Wiegmann, 1828 | 1,2,3,5 | LC | Pr | L (6) | 1 | 1938 |
|
FAMILY DACTYLOIDAE (1) | |||||||
Anolis nebulosus (Wiegmann, 1834) | 1,2,4 | LC | NL | M (13) | 1 | 1940 |
|
FAMILY GECKONIDAE (1) | |||||||
Hemidactylus frenatus Duméril & Bribon, 1836 | IN | IN | IN | IN | IN | 1998 |
|
FAMILY HELODERMATIDAE (1) | |||||||
Heloderma horridum (Wiegmann, 1829) | 4 | LC | A | M (11) | 3 | 1933 |
|
FAMILY IGUANIDAE (1) | |||||||
Ctenosaura pectinata (Wiegmann, 1834) | 4 | NE | A | H (15) | 1 | 1982 |
|
FAMILIY PHRYNOSOMATIDAE (19) | |||||||
Phrynosoma orbiculare (Linnaeus, 1758) | 1,2,5,6 | LC | A | M (12) | 1 | 1888 |
|
Sceloporus aeneus Wiegmann, 1828 | 5,6 | LC | NL | M (13) | 1 | 1921 |
|
Sceloporus anahuacus Lara-Góngora, 1983 | 1,2,3 | LC | NL | H (15) | 1 | 1979 |
|
Sceloporus bicanthalis Smith, 1937 | 5 | LC | NL | M (13) | 1 | 1937 |
|
Sceloporus dugesii Bocourt, 1874 | 2,5 | LC | NL | M (13) | 1 | 1983 |
|
Sceloporus gadoviae Boulenger, 1905 | 4 | LC | NL | M (11) | 1 | 1996 |
|
Sceloporus grammicus Wiegmann, 1828 | 1,2,3,6 | LC | Pr | L (9) | 1 | 1888 |
|
Sceloporus horridus Wiegmann, 1834 | 4 | LC | NL | M (11) | 1 | 1951 |
|
Sceloporus megalepidurus Smith, 1934 | 4 | VU | Pr | H (14) | 1 | 1971 |
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Sceloporus melanorhinus Bocourt, 1876 | 4 | LC | NL | L (9) | 3 | 1977 |
|
Sceloporus mucronatus Cope, 1885 | 2,3,5 | LC | NL | M (13) | 1 | 1939 |
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Sceloporus ochoterenae Smith, 1934 | 4 | LC | NL | M (12) | 1 | 1992 |
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Sceloporus palaciosi Lara-Góngora, 1983 | 1,2,3 | LC | NL | H (15) | 1 | 1976 |
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Sceloporus pyrocephalus Cope, 1864 | 4 | LC | NL | M (12) | 1 | 1982 |
|
Scelopours scalaris Wiegmann, 1828 | 5,6 | LC | NL | M (12) | 1 | 1888 |
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Sceloporus spinosus Wiegmann, 1828 | 1,2,5,6 | LC | NL | M (12) | 1 | 1922 |
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Sceloporus sugillatus Smith, 1942 | 1,2,3 | LC | NL | H (16) | 1 | 1939 |
|
Sceloporus torquatus Wiegmann, 1828 | 1,2,3,5,6 | LC | NL | M (11) | 1 | 1888 |
|
Urosaurus bicarinatus (Duméril, 1856) | 4 | LC | NL | M (12) | 1 | 1930 |
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FAMILY PHYLLODACTYLIDAE (1) | |||||||
Phyllodactylus lanei Smith, 1935 | 4 | LC | NL | H (15) | 1 | 1981 |
|
FAMILY SCINCIDAE (6) | |||||||
Marisora brachypoda (Taylor, 1956) | 4 | LC | NL | L (6) | 3 | 1882 |
|
Plestiodon brevirostris (Günther, 1860) | 1,2,3 | LC | NL | M (11) | 1 | 1942 |
KU |
Plestiodon copei (Taylor, 1933) | 1,2,3 | LC | Pr | H (14) | 1 | 1932 |
|
Plestiodon dugesii (Thominot, 1883) | 1,2,3 | VU | Pr | H (16) | 1 | 1954 |
KU |
Plestiodon indubitus (Taylor, 1933) | 1,2,3 | NE | NL | H (15) | 1 | 1932 |
|
Plestiodon lynxe (Wiegmann, 1834) | 1,2,3 | LC | Pr | M (10) | 1 | 1974 | UTA 4182 |
FAMILY TEIIDAE (5) | |||||||
Aspidoscelis communis (Cope, 1878) | 4 | LC | Pr | H (14) | 1 | 2009 |
|
Aspidoscelis costatus (Cope, 1878) | 4 | LC | Pr | M (11) | 1 | 1941 |
|
Aspidoscelis deppii (Wiegmann, 1834) | 4 | LC | NL | L (8) | 3 | 1977 |
|
Aspidoscelis gularis (Baird & Girard, 1852) | 4 | LC | NL | L (9) | 4 | 1930 |
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Aspidoscelis sackii (Wiegmann, 1834) | 4 | LC | NL | H (14) | 1 | 1966 |
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SUBORDER SERPENTES | |||||||
FAMILY BOIDAE (1) | |||||||
Boa sigma Smith, 1943 | 4 | NE | NL | H (15) | 1 | 1985 |
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FAMILY COLUBRIDAE (21) | |||||||
Conopsis biserialis (Taylor & Smith, 1942) | 1,2,3,6 | LC | A | M (13) | 1 | 1932 |
|
Conopsis lineata (Kennicott, 1859) | 1,2,3,6 | LC | NL | M (13) | 1 | 1859 |
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Conopsis nasus (Günther, 1858) | 1,2,3 ,6 | LC | NL | M (11) | 1 | 1921 |
|
Drymarchon melanurus (Duméril, Bibron & Duméril, 1854) | 4 | LC | NL | L (6) | 3 | 1975 |
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Drymobius margaritiferus (Schlegel, 1837) | 4 | LC | NL | L (6) | 3 | 1939 |
|
Lampropeltis polyzona Cope, 1860 | 1,2,3,4,5 | LC | NL | L (7) | 1 | 1943 |
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Leptophis diplotropis (Günther, 1872) | 4 | LC | A | H (14) | 1 | 1978 |
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Masticophis mentovarius (Duméril, Bibron & Duméril, 1854) | 4 | LC | A | L (6) | 3 | 1960 |
KU |
Oxybelis aeneus (Wagler, 1824) | 4 | LC | NL | L (5) | 4 | 1985 |
|
Pituophis deppei (Dumeril, 1853) | 1,2,3,4,6 | LC | A | H (14) | 1 | 1853 | Dumeril 1853 |
Pituophis lineaticollis (Cope, 1861) | 1,2,3,4,5 | LC | NL | L (8) | 3 | 1940 |
|
Pseudoficimia frontalis (Cope, 1864) | 4 | LC | NL | M (13) | 1 | 1951 |
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Salvadora bairdi Jan & Sordelli, 1860 | 1,2,3,4,5,6 | LC | Pr | H (15) | 1 | 1888 |
|
Salvadora mexicana (Duméril, Bibron & Duméril, 1854) | 4 | LC | Pr | H (15) | 1 | 1982 |
|
Senticolis triaspis (Cope, 1866) | 1,2,4,5 | LC | NL | L (6) | 3 | 1943 |
|
Tantilla bocourti (Günther, 1895) | 1,2,5 | LC | NL | L (9) | 1 | 1960 |
KU |
Tantilla calamarina Cope, 1866 | 4 | LC | Pr | M (12) | 1 | 1981 |
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Tantilla deppei (Bocourt, 1883) | 4 | LC | A | M (13) | 1 | 1977 |
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Tantilla rubra Cope, 1875 | 1,2,3,5 | LC | Pr | L (5) | 3 | 2009 |
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Trimorphodon biscutatus (Duméril, Bibron & Duméril, 1854) | 4 | NE | NL | L (7) | 3 | 1983 |
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Trimorphodon tau Cope, 1870 | 4 | LC | NL | M (13) | 1 | 1943 |
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FAMILY DIPSADIDAE (12) | |||||||
Conophis vittatus Peters, 1860 | 4 | LC | NL | M (11) | 3 | 2004 |
|
Diadophis punctatus (Linnaeus, 1766) | 1,2,3,6 | LC | NL | L (4) | 2 | 1937 |
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Enulius flavitorques (Cope, 1868) | 4 | LC | NL | L (5) | 3 | 1951 |
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Geophis bicolor Günther, 1868 | 4 | DD | Pr | H (15) | 1 | 1992 |
|
Geophis sieboldi (Jan, 1862) | 4 | DD | Pr | M (13) | 1 | 1991 |
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Imantodes gemmistratus (Cope, 1861) | 4 | LC | Pr | L (6) | 3 | 1951 |
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Leptodeira maculata (Hallowell, 1861) | 4,6 | LC | Pr | L (7) | 1 | 1965 |
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Leptodeira septentrionalis (Kennicott, 1859) | 4 | LC | NL | L (8) | 4 | 1992 |
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Leptodeira splendida Günther, 1895 | 4 | LC | NL | H (14) | 1 | 1976 |
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Rhadinaea hesperia Bailey, 1940 | 4 | LC | Pr | M (10) | 1 | 1973 |
|
Rhadinaea laureata (Günther, 1868) | 1,2,3 | LC | NL | M (12) | 1 | 1952 |
KU |
Rhadinaea taeniata (Peters, 1863) | 1,2 | LC | NL | M (13) | 1 | 1979 |
|
FAMILY ELAPIDAE (3) | |||||||
Micrurus browni Schmidt & Smith, 1943 | 1,2 | LC | Pr | L (8) | 3 | 1954 |
KU |
Micrurus laticollaris Peters, 1870 | 4 | LC | Pr | H (14) | 1 | 1986 |
|
Micrurus tener Baird & Girard, 1953 | 1,4 | LC | NL | M (11) | 2 | 1943 |
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FAMILY LEPTOTYPHLOPIDAE (2) | |||||||
Epictia bakewelli (Oliver, 1937) | 4 | NE | NL | NE | 1 | 1985 |
|
Rena maxima (Loveridge, 1932) | 4 | LC | NL | M (11) | 1 | 1960 |
KU |
FAMILY NATRICIDAE (7) | |||||||
Storeria storerioides (Cope, 1866) | 1,2,3 | LC | NL | M (11) | 1 | 1938 |
|
Thamnophis cyrtopsis (Kennicott, 1860) | 1,2,3,4,6 | LC | A | L (7) | 4 | 1892 |
|
Thamnophis eques (Reuss, 1834) | 1,2,3,4,6 | LC | A | L (8) | 2 | 1904 |
|
Thamnophis melanogaster (Wiegmann, 1830) | 1,2,3,6 | EN | A | H (15) | 1 | 1888 |
|
Thamnophis pulchrilatus (Cope, 1885) | 1,2,3,4 | LC | NL | H (15) | 1 | 1888 | |
Thamnophis scalaris Cope, 1861 | 1,2,3,5 | LC | A | H (14) | 1 | 1888 | |
Thamnohis scaliger (Jan, 1863) | 1,2,3,5,6 | VU | A | H (15) | 1 | 1939 |
|
FAMILY TYPHLOPIDAE (1) | |||||||
Indotyphlops braminus (Daudin, 1803) | IN | IN | IN | IN | IN | 1997 |
|
FAMILY VIPERIDAE (10) | |||||||
Crotalus aquilus Klauber, 1952 | 1,2,3,4,6 | LC | Pr | H (16) | 1 | 1982 |
|
Crotalus atrox Baird & Girard, 1853 | 5 | LC | Pr | L (9) | 2 | 2004 |
|
Crotalus culminatus Klauber, 1952 | 4 | NE | NL | H (15) | 1 | 1888 |
|
Crotalus molossus Baird & Girard, 1853 | 1,2,3,6 | LC | Pr | L (8) | 2 | 1888 |
|
Crotalus polystictus (Cope, 1865) | 1,2,3,4 | LC | Pr | H (16) | 1 | 1888 |
|
Crotalus ravus Cope, 1865 | 1,2,3,4,6 | LC | A | H (14) | 1 | 1938 |
|
Crotalus scutulatus (Kennicott, 1861) | 5 | LC | Pr | M (11) | 2 | 1967 |
|
Crotalus tlaloci Bryson, Linkem, Dorcas, Lathrop, Jones, Alvarado-Días, Grünwald & Murphy, 2014 | 1,2,3,4 | NE | NL | H (16) | 1 | 2014 |
|
Crotalus transversus Taylor, 1944 | 2,3 | LC | P | H (17) | 1 | 1973 |
KU |
Crotalus triseriatus (Wagler, 1830) | 1,2,3,4,6 | LC | NL | H (16) | 1 | 1940 |
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ORDER TESTUDINES | |||||||
EMYDIDAE (1) | |||||||
Trachemys venusta (Gray, 1855) | 4 | NE | NL | M (13) | 3 | 1939 |
|
FAMILY GEOEMYDIDAE (1) | |||||||
Rhinoclemmys rubida (Cope, 1870) | 4 | NT | Pr | H (14) | 1 | 1983 |
|
FAMILY KINOSTERNIDAE (2) | |||||||
Kinosternon hirtipes (Wagler, 1830) | 1,4,5,6 | LC | Pr | M (10) | 2 | 1888 |
|
Kinosternon integrum LeConte, 1854 | 4 | LC | Pr | M (11) | 1 | 1888 |
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In the State of Mexico, the percentage of herpetofaunal species found in the Oak (51.7%), Pine-oak (55.8%), Pine (44.9%), and Tropical Deciduous Forest (51.7%) vegetation types are relatively equal (Table
List of amphibian and reptile species that potentially occur in the State of Mexico.
Region in the State of Mexico where it likely occurs | |
---|---|
CLASS AMPHIBIA | |
ORDER ANURA | |
Family Craugastoridae | |
Craugastor rhodopis (Cope, 1867) | southern |
Family Hylidae | |
Scinax staufferi (Cope, 1865) | southern |
CLASS REPTILIA | |
ORDER SQUAMATA | |
SUBORDER AMPHISBAENIA | |
Family Bipedidae | |
Bipes canaliculatus Latreille, 1801 | extreme southwestern |
SUBORDER LACERTILIA | |
Family Anguidae | |
Gerrhonotus ophiourus Cope, 1867 | eastern and southern |
Family Eublepharidae | |
Coleonyx elegans Gray, 1845 | extreme southwestern |
Family Phrynosomatidae | |
Phrynosoma asio Cope, 1864 | extreme southwestern |
Sceloporus minor Cope, 1885 | northern |
Sceloporus siniferus Cope, 1870 | extreme southwestern |
Sceloporus utiformis Cope, 1864 | extreme southwestern |
Family Phyllodactylidae | |
Phyllodactylus bordai Taylor, 1942 | extreme southwestern |
Phyllodactylus tuberculosus Wiegmann, 1834 | extreme southwestern |
Family Teiidae | |
Holcosus sinister (Wiegmann, 1834) | extreme southwestern |
SUBORDER SERPENTES | |
Family Colubridae | |
Ficimia publia (Cope, 1866) | extreme southwestern |
Lampropeltis ruthveni Blanchard, 1920 | northern |
Mastigodryas melanolomus (Cope, 1868) | extreme southwestern |
Sonora michoacanensi (Dugès, 1884) | western and southwestern |
Family Dipsadidae | |
Pseudoleptodeira latifasciata (Günther, 1894) | extreme southwestern |
Tropidodipsas zweifeli (Liner & Wilson, 1970) | extreme southwestern |
Family Loxocemidae | |
Loxocemus bicolor Cope, 1861 | extreme southwestern |
Family Viperidae | |
Agkistrodon bilineatus Günther, 1863 | extreme southwestern |
ORDER TESTUDINES | |
Family Kinosternidae | |
Kinosternon scorpioides (Linnaeus, 1766) | western and southwestern |
Of the amphibian and reptile species in the State of Mexico, 20.1% are IUCN listed (i.e., Vulnerable, Near Threatened, or Endangered), 18.4% are placed in a protected category by SEMARNAT (excluding NL and Pr, this last category is equivalent to the LC category of IUCN), and 34.9% are categorized as high risk by the EVS (Table
Proportion of A) amphibians and B) reptiles listed in protected categories on the IUCN Red List, SEMARNAT, and high EVS for the State of Mexico. Green is proportion in Data Deficient and Least Concern (IUCN); Not Listed and Subject to Special Protection (we regarded the category of Subject to Special Protection in SEMARNAT equivalent to Least Concern in IUCN) (SEMARNAT); or low or medium EVS. Red is percentage in protected categories or high EVS. N is the number of species assessed.
Summary of native species present in the State of Mexico by family, order or suborder, and class. Status summary indicates the number of species found in each IUCN conservation status in the order DD, LC, VU, NT, EN, CR (see Table
Scientific name | Genera | Species | IUCN | x̅ EVS | SEMARNAT |
---|---|---|---|---|---|
DD, LC, VU, NT, EN, CR | NL, Pr, A, P | ||||
CLASS AMPHIBIA | |||||
ORDER ANURA | 15 | 32 | 1,24,2,1,3,1 | 10.3 | 20,9,2,1 |
Bufonidae | 3 | 5 | 0,4,0,0,1,0 | 10.4 | 5,0,0,0 |
Craugastoridae | 1 | 4 | 0,2,1,0,1,0 | 11.25 | 4,0,0,0 |
Eleutherodactylidae | 1 | 4 | 1,2,1,0,0,0 | 14.3 | 2,2,0,0 |
Hylidae | 5 | 9 | 0,8,0,0,1,0 | 9.3 | 6,2,1,0 |
Leptodactylidae | 1 | 1 | 0,1,0,0,0,0 | 6 | 0,1,0,0 |
Microhylidae | 1 | 1 | 0,1,0,0,0,0 | 4 | 0,1,0,0 |
Phyllomedusidae | 1 | 1 | 0,1,0,0,0,0 | 13 | 0,1,0,0 |
Ranidae | 1 | 6 | 0,4,0,1,0,1 | 11.2 | 2,2,1,1 |
Scaphiopodidae | 1 | 1 | 0,1,0,0,0,0 | 3 | 1,0,0,0 |
ORDER CAUDATA | 5 | 16 | 1,2,2,1,5,5 | 14.8 | 2,7,7,0 |
Ambystomatidae | 1 | 8 | 1,1,0,0,2,4 | 13.5 | 0,5,3,0 |
Plethodontidae | 4 | 8 | 0,1,2,1,3,1 | 16.1 | 2,2,4,0 |
SUBTOTAL | 20 | 48 | 2,26,4,2,8,6 | 11.8 | 22,16,9,1 |
CLASS REPTILIA | |||||
ORDER SQUAMATA | 40 | 95 | 2,79,3,0,4,0 | 11.5 | 53,25,15,2 |
SUBORDER LACERTILIA | 13 | 39 | 0,32,2,0,3,0 | 12.4 | 25,9,4,1 |
Anguidae | 3 | 5 | 0,2,0,0,3,0 | 13.2 | 1,2,1,1 |
Dactyloidae | 1 | 1 | 0,1,0,0,0,0 | 13 | 1,0,0,0 |
Helodermatidae | 1 | 1 | 0,1,0,0,0,0 | 11 | 0,0,1,0 |
Iguanidae | 1 | 1 | 0,0,0,0,0,0 | 15 | 0,0,1,0 |
Phrynosomatidae | 3 | 19 | 0,18,1,0,0,0 | 12.4 | 16,2,1,0 |
Phyllodactylidae | 1 | 1 | 0,1,0,0,0,0 | 15 | 1,0,0,0 |
Scincidae | 2 | 6 | 0,4,1,0,0,0 | 12 | 3,3,0,0 |
Teiidae | 1 | 5 | 0,5,0,0,0,0 | 11.2 | 3,2,0,0 |
SUBORDER SERPENTES | 27 | 56 | 2,47,1,0,1,0 | 11 | 28,16,11,1 |
Boidae | 1 | 1 | 0,0,0,0,0,0 | 15 | 1,0,0,0 |
Colubridae | 13 | 21 | 0,20,0,0,0,0 | 10 | 12,4,5,0 |
Dipsadidae | 7 | 12 | 2,10,0,0,0,0 | 9.8 | 7,5,0,0 |
Elapidae | 1 | 3 | 0,3,0,0,0,0 | 11 | 1,2,0,0 |
Leptotyphlopidae | 2 | 2 | 0,1,0,0,0,0 | 11 | 2,0,0,0 |
Natricidae | 2 | 7 | 0,5,1,0,1,0 | 11.5 | 2,0,5,0 |
Viperidae | 1 | 10 | 0,8,0,0,0,0 | 13.8 | 3,5,1,1 |
ORDER TESTUDINES | 3 | 4 | 0,2,0,1,0,0 | 12 | 1,3,0,0 |
Emydidae | 1 | 1 | 0,0,0,0,0,0 | 13 | 1,0,0,0 |
Geoemydidae | 1 | 1 | 0,0,0,1,0,0 | 14 | 0,1,0,0 |
Kinosternidae | 1 | 2 | 0,2,0,0,0,0 | 10.5 | 0,2,0,0 |
SUBTOTAL | 43 | 99 | 2,81,3,1,4,0 | 11.6 | 54,28,15,2 |
TOTAL | 63 | 147 | 4107,7,3,12,6 | 11.7 | 76,44,24,3 |
We summarized the conservation status of amphibian and reptile taxa in each vegetation type found in the State of Mexico to determine the vegetation types that support species of particular conservation concern (Table
Overall, the State of Mexico shares the most species (76.9%) with Michoacán (Table
Summary of the numbers of species shared between the State of Mexico and neighboring Mexican states (not including introduced species). The percent of the State of Mexico species shared by a neighboring state are given in parentheses. – indicates either the State of Mexico or the neighboring state has no species in the taxonomic group, or none of that specific taxon is shared between the states, thus no value for shared species is provided.
Taxon | State of Mexico | Michoacán | Morelos | Puebla | Guerrero | Hidalgo | Querétaro | Mexico City |
---|---|---|---|---|---|---|---|---|
CLASS AMPHIBIA | 48 | 35 (72.9) | 33 (68.8) | 27 (56.3) | 26 (55.3) | 20 (41.7) | 16 (33.3) | 16 (33.3) |
ORDER ANURA | 32 | 28 (87.5) | 26 (81.3) | 23 (71.9) | 23 (71.9) | 16 (50.0) | 13 (40.6) | 8 (25.0) |
Bufonidae | 5 | 5 (100) | 5 (100) | 5 (100) | 4 (80.0) | 3 (60.0) | 3 (60.0) | 1 (20.0) |
Craugastoridae | 4 | 3 (75.0) | 4 (100) | 3 (75.0) | 4 (100) | 1 (25.0) | 1 (25.0) | 1 (25.0) |
Eleutherodactylidae | 4 | 3 (75.0) | 3 (75.0) | 1 (25.0) | 2 (50.0) | 1 (25.0) | 1 (25.0) | – |
Hylidae | 9 | 8 (88.9) | 7 (77.8) | 7 (77.8) | 7 (77.8) | 5 (55.6) | 3 (33.3) | 3 (33.3) |
Leptodactylidae | 1 | 1 (100) | 0 | 1 (100) | 1 (100) | 1 (100) | – | – |
Microhylidae | 1 | 1 (100) | 1 (100) | 1 (100) | 1 (100) | 1 (100) | 1 (100) | – |
Phyllomedusidae | 1 | 1 (100) | 1 (100) | 1 (100) | 1 (100) | – | – | – |
Ranidae | 6 | 5 (83.3) | 4 (66.7) | 3 (50.0) | 2 (33.3) | 3 (50.0) | 3 (50.0) | 2 (33.3) |
Scaphiopodidae | 1 | 1 (100) | 1 (100) | 1 (100) | 1 (100) | 1 (100) | 1 (100) | 1 (100) |
ORDER CAUDATA | 16 | 7 (43.8) | 7 (43.8) | 4 (25.0) | 3 (18.8) | 4 (25.0) | 3 (18.8)) | 8 (50.0) |
Ambystomatidae | 8 | 4 (50.0) | 1 (12.5) | 1 (12.5) | 1 (12.5) | 1 (12.5) | 1 (12.5) | 2 (25.0) |
Plethodontidae | 8 | 3 (37.5) | 6 (75.0) | 3 (37.5) | 2 (25.0) | 3 (37.5) | 2 (25.0) | 6 (75.0) |
CLASS REPTILIA | 99 | 78 (78.8) | 73 (71.8) | 71 (71.7) | 65 (65.7) | 47 (47.5) | 45 (45.5) | 43 (43.4) |
ORDER SQUAMATA | 95 | 75 (78.9) | 71 (74.7) | 69 (72.6) | 63 (66.3) | 44 (46.3) | 43 (45.3) | 41 (43.2) |
SUBORDER LACERTILIA | 39 | 28 (71.8) | 29 (74.4) | 26 (66.7) | 26 (66.7) | 12 (30.8) | 10 (25.6) | 14 (35.9) |
Anguidae | 5 | 3 (60.0) | 4 (80.0) | 2 (40.0) | 3 (60.0) | 1 (20.0) | 1 (20.0) | 1 (20.0) |
Dactyloidae | 1 | 1 (100) | 1 (100) | – | 1 (100) | – | – | – |
Helodermatidae | 1 | 1 (100) | 1 (100) | 1 (100) | 1 (100) | – | – | – |
Iguanidae | 1 | 1 (100) | 1 (100) | 1 (100) | 1 (100) | – | – | – |
Phrynosomatidae | 19 | 12 (63.2) | 14 (73.7) | 15 (78.9) | 12 (63.2) | 9 (47.4) | 7 (36.8) | 10 (52.6) |
Phyllodactylidae | 1 | 1 (100) | – | – | 1 (100) | – | – | – |
Scincidae | 6 | 4 (66.7) | 4 (66.7) | 4 (66.7) | 3 (50.0) | 1 (16.7) | 1 (16.7) | 2 (33.3) |
Teiidae | 5 | 5 (100) | 4 (80.0) | 3 (60.0) | 4 (80.0) | 1 (20.0) | 1 (20.0) | 1 (20.0) |
SUBORDER SERPENTES | 56 | 47 (83.9) | 42 (75.0) | 43 (76.8) | 37 (66.1) | 32 (57.1) | 33 (58.9) | 27 (48.2) |
Boidae | 1 | 1 (100) | 1 (100) | 1 (100) | 1 (100) | – | – | – |
Colubridae | 21 | 19 (90.5) | 19 (90.5) | 20 (95.2) | 18 (85.7) | 13 (61.9) | 14 (66.7) | 9 (42.9) |
Dipsadidae | 12 | 11 (91.7) | 8 (66.7) | 7 (58.3) | 8 (66.6) | 5 (41.7) | 4 (33.3) | 4 (33.3) |
Elapidae | 3 | 2 (66.7) | 2 (66.7) | 2 (66.7) | 2 (66.6) | 1 (33.3) | 1 (33.3) | 1 (33.3) |
Leptotyphlopidae | 2 | 2 (100) | 1 (50.0) | 1 (50.0) | 2 (100) | 1 (50.0) | 1 (50.0) | – |
Natricidae | 7 | 7 (100) | 4 (57.1) | 6 (85.7) | 3 (42.9) | 6 (85.7) | 6 (85.7) | 7 (100) |
Viperidae | 10 | 5 (50.0) | 7 (70.0) | 6 (60.0) | 3 (30.0) | 6 (60.0) | 7 (70.0) | 6 (60.0) |
ORDER TESTUDINES | 4 | 3 (75.0) | 2 (50.0) | 2 (50.0) | 2 (50.0) | 3 (75.0) | 2 (50.0) | 2 (50.0) |
Emydidae | 1 | – | – | 1 (100) | – | 1 (100) | – | – |
Geoemydidae | 1 | 1 (100) | – | – | 1 (100) | – | – | – |
Kinosternidae | 2 | 2 (100) | 2 (100) | 1 (50.0) | 1 (50.0) | 2 (100) | 2 (100) | 2 (100) |
TOTAL | 147 | 113 (76.9) | 106 (72.1) | 98 (66.7) | 91 (61.9) | 67 (45.6) | 61 (41.5) | 59 (40.1) |
We thank Jesús Sigala and John Murphy for very helpful comments that greatly improved the manuscript. Support for this study was provided by Dirección General de Asuntos del Personal Académico, Programa de Apoyo a Proyectos de Investigación e Innovación Tecnológica (DGAPA-PAPIIT) through the Project IN215418. We are grateful to Alejandra Núñez Merchand from the National Commission for the Understanding and Use of Biodiversity (CONABIO) for kindly creating and providing the municipality, topographic, physiographic, climate, and vegetation maps used in this publication and for generating the state border lengths of the State of Mexico’s neighboring states, and to Isabel Cruz, also from CONABIO, for providing the satellite images of the State of Mexico. We are grateful to Alan Resetar and Joshua Mata from the Field Museum of Natural History, Chicago, Illinois; Emily M. Braker from the University of Colorado Museum, University of Colorado at Boulder; Jimmy McGuire, Carol Spencer, and David Wake from the Museum of Vertebrate Zoology at Berkeley, University of California at Berkeley; and D. Dickey and D.A. Kizirian from the American Museum of Natural History, New York. Eric Centenero-Alcalá kindly allowed us to use his photographs in Figure
Museum collections included in the VertNet.org database records of the State of Mexico amphibians and reptiles that house specimens of the first record of a species in the State of Mexico.
KU
UTAMM Merriam Museum, University of Texas Arlington;