Sceloporus cowlesi
Lowe and Norris, 1956
Southwestern Fence Lizard
Identity
Unique IDELEMENT_GLOBAL.2.105344
Element CodeARACF14132
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVertebrate Animal
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomAnimalia
PhylumCraniata
ClassReptilia
OrderSquamata
FamilyPhrynosomatidae
GenusSceloporus
SynonymsSceloporus undulatus cowlesiLowe and Norris, 1956
Concept ReferenceLeaché, A. D., and T. W. Reeder. 2002. Molecular systematics of the eastern fence lizard (Sceloporus undulatus): a comparison of parsimony, likelihood, and Bayesian approaches. Systematic Biology 51:44-68.
Taxonomic CommentsSceloporus cowlesi formerly was included in S. undulatus. The traditionally recognized Sceloporus undulatus is morphologically highly variable (e.g., see Stebbins 1985, Conant and Collins 1991, Hammerson 1999).
Leaché and Reeder (2002) examined range-wide mtDNA variation and identified at least four apparently monophyletic (but morphologically highly variable) groups, which they proposed as species under the evolutionary species concept (Eastern group: east of Mobile Bay; Central group: east of the Rockies and west of Mobile Bay; Western group: southern Wyoming to central Arizona and northern New Mexico; Southwestern group: eastern Arizona and central New Mexico to northern Mexico and western Texas). All of the groups are discordant with recognized subspecies circumscriptions. For example, the Central group encompasses six nominal subspecies ranging from the foothills of the Rocky Mountains in Colorado to the Gulf Coast of southern Mississippi. Populations of the morphologically distinctive subspecies erythrocheilus in central Colorado grouped with subspecies garmani (Central group) rather than with populations of erythrocheilus in south-central Colorado (Western group). Leaché and Reeder (2002) tentatively proposed the following names: eastern group, S. undulatus; central group, S. consobrinus; western group, S. tristichus; southwestern group, S. cowlesi. However, Leaché and Reeder identified no diagnostic characters for any of the proposed species, and the distributions of proposed species were only coarsely mapped and do not correspond closely with the distributions of previously recognized subspecies, leaving in doubt the specific identities of many Sceloporus populations.
Further integrated study of genetic variation, using mitochindrial and nuclear DNA, and more detailed genetic examination of various geographic areas (Niewiarowski et al. 2004; Leaché and Cole 2007; Leaché 2009) has helped clarify relationships among "S. undulatus" populations. Recognition of the four species proposed by Leaché and Reeder (2002) seems to be a justifiable change in the treatment of this complex, but the precise distributions of the taxa near some clade boundaries remain problematic. Leaché and Cole (2007) acknowledged the challenges imposed by apparent decoupling of morphological, karyotypic, and mtDNA divergence that may occur among populations in this complex and noted that conclusions about the number of species in the S. undulatus complex are directly linked to the particular "threshold' one imposes to define species status.
Rosenblum (2006) found both phylogenetic mixing of haplotypes between light and dark forms and evidence of gene flow between them. Rosenblum and Harmon (2010) found that fence lizards from the White Sands exhibited discordant patterns of morphological and genetic differentiation from their counterparts on adjacent darker soils and concluded that the populations have made incomplete progress toward speciation (Crother 2017).
Leaché and Cole (2007) presented evidence for hybridization between S. cowlesi and S. tristichus in an ecotone in eastern Arizona.
Conservation Status
Rank MethodExpertise without calculation
Review Date2013-07-04
Change Date2013-07-04
Edition Date2013-07-10
Number of Occurrences81 to >300
Range Extent CommentsAccording to Leaché and Reeder (2002), the range of Sceloporus cowlesi includes southern and eastern Arizona, New Mexico, western Texas, and northern Chihuahua, Mexico. Leaché and Reeder (2002) provided only coarse-scale range maps and did not include distributional details for areas where the range of this species adjoins or approaches the ranges of S. consobrinus or S. tristichus. Leaché and Cole (2007) documented hybridization between S. cowlesi and S. tristichus in Arizona. Powell et al. (2016) indicated the range as extending from eastern Arizona and western, central, and southern New Mexico southward through western Texas to northcentral Mexico.
Occurrences CommentsThis species is represented by a large number of occurrences (subpopulations) and locations (as defined by IUCN).
Ecology & Habitat
Habitat
Habitat in most areas consists of openly wooded, shrubby, or rocky areas. Usually these lizards are in open/sunny situations.
Terrestrial HabitatsForest/WoodlandForest EdgeWoodland - HardwoodWoodland - ConiferWoodland - MixedShrubland/chaparralBare rock/talus/screeCliff
Palustrine HabitatsRiparian
Other Nations (1)
United StatesN5
| Province | Rank | Native |
|---|
| New Mexico | S4 | Yes |
| Navajo Nation | S5 | Yes |
| Texas | SNR | Yes |
| Arizona | S4 | Yes |
Roadless Areas (51)
Arizona (12)
| Area | Forest | Acres |
|---|
| Butterfly Roadless Area | Coronado National Forest | 42,296 |
| Cdo Wsa | Coronado National Forest | 1,955 |
| Centerfire | Apache-Sitgreaves National Forests | 13,130 |
| Chiricahua | Coronado National Forest | 76,876 |
| Galiuro | Coronado National Forest | 28,333 |
| Hell Hole | Apache-Sitgreaves National Forests | 15,512 |
| Middle Dragoon Roadless | Coronado National Forest | 10,543 |
| Nolan | Apache-Sitgreaves National Forests | 6,780 |
| Oracle Roadless | Coronado National Forest | 22,365 |
| Pinaleno | Coronado National Forest | 130,920 |
| Santa Teresa | Coronado National Forest | 8,929 |
| Tumacacori | Coronado National Forest | 44,594 |
New Mexico (39)
| Area | Forest | Acres |
|---|
| Alamo Canyon | Santa Fe National Forest | 8,639 |
| Apache Kid Contiguous | Cibola National Forest | 67,542 |
| Aspen Mountain | Gila National Forest | 23,784 |
| Black Canyon | Santa Fe National Forest | 1,922 |
| Caja | Santa Fe National Forest | 5,304 |
| Capitan Mountains | Lincoln National Forest | 14,069 |
| Carrizo Mountain | Lincoln National Forest | 17,280 |
| Contiguous To Black & Aldo Leopold Wilderness | Gila National Forest | 111,883 |
| Contiguous To Gila Wilderness & Primitive Area | Gila National Forest | 79,049 |
| Devils Creek | Gila National Forest | 89,916 |
| Dry Creek | Gila National Forest | 26,719 |
| Frisco Box | Gila National Forest | 38,979 |
| Goat Spring | Cibola National Forest | 5,755 |
| Guaje Canyon | Santa Fe National Forest | 6,104 |
| Hell Hole | Gila National Forest | 19,553 |
| Jefferies Canyon | Lincoln National Forest | 8,934 |
| Juan de Gabaldon Grant | Santa Fe National Forest | 8,023 |
| Last Chance Canyon | Lincoln National Forest | 8,934 |
| Lemitas | Santa Fe National Forest | 8,129 |
| Little Tesuque | Santa Fe National Forest | 815 |
| Meadow Creek | Gila National Forest | 34,167 |
| Mother Hubbard | Gila National Forest | 5,895 |
| Nichols Reservoir | Santa Fe National Forest | 1,518 |
| Nolan | Gila National Forest | 13,051 |
| Ortega Peak | Lincoln National Forest | 11,545 |
| Pacheco Canyon | Santa Fe National Forest | 1,012 |
| Peloncillo (NM) | Coronado National Forest | 43,339 |
| Rendija | Santa Fe National Forest | 2,176 |
| Ryan Hill | Cibola National Forest | 34,201 |
| San Jose | Cibola National Forest | 16,950 |
| Sawyers Peak | Gila National Forest | 59,743 |
| Scott Mesa | Cibola National Forest | 39,515 |
| South Guadalupe Mountains | Lincoln National Forest | 20,930 |
| Tesuque Creek | Santa Fe National Forest | 810 |
| The Hub | Gila National Forest | 7,498 |
| Thompson Peak | Santa Fe National Forest | 33,001 |
| Virgin Canyon | Santa Fe National Forest | 6,068 |
| Wahoo Mountain | Gila National Forest | 23,122 |
| West Face Sacramento Mountains | Lincoln National Forest | 41,176 |
References (9)
- Collins, J. T. 1990. Standard common and current scientific names for North American amphibians and reptiles. 3rd ed. Society for the Study of Amphibians and Reptiles. Herpetological Circular No. 19. 41 pp.
- Crother, B. I. (editor). 2008. Scientific and standard English names of amphibians and reptiles of North America north of Mexico, with comments regarding confidence in our understanding. Sixth edition. Society for the Study of Amphibians and Reptiles Herpetological Circular 37:1-84. Online with updates at: http://www.ssarherps.org/pages/comm_names/Index.php
- Crother, B. I. (editor). 2012. Scientific and standard English names of amphibians and reptiles of North America north of Mexico, with comments regarding confidence in our understanding. 7th edition. SSAR Herpetological Circular 39:1-92.
- Crother, B. I. (editor). 2017. Scientific and standard English names of amphibians and reptiles of North America north of Mexico, with comments regarding confidence in our understanding. 8th edition. SSAR Herpetological Circular 43:1-104. [Updates in SSAR North American Species Names Database at: https://ssarherps.org/cndb]
- Leaché, A. D., and C. J. Cole. 2007. Hybridization between multiple fence lizard lineages in an ecotone: locally discordant variation in mitochondrial DNA, chromosomes, and morphology. Molecular Ecology 16:1035-1054.
- Leaché, A. D., and T. W. Reeder. 2002. Molecular systematics of the eastern fence lizard (<i>Sceloporus undulatus</i>): a comparison of parsimony, likelihood, and Bayesian approaches. Systematic Biology 51:44-68.
- Powell, R., R. Conant, and J. T. Collins. 2016. Peterson Field Guide to Reptiles and Amphibians of Eastern and Central North America, fourth edition. Houghton Mifflin Harcourt, Boston and New York. 512 pp.
- Rosenblum, E. B. 2006. Convergent evolution and divergent selection: lizards at the White Sands ecotone. American Naturalist 167:1-15.
- Rosenblum, E. B., and L. J. Harmon. 2010. "Same same but different": replicated ecological speciation at White Sands. Evolution 65:946-960.