Phrynosoma platyrhinos

Girard, 1852

Desert Horned Lizard

G4Apparently Secure Found in 69 roadless areas NatureServe Explorer →
G4Apparently SecureGlobal Rank
Least concernIUCN
MediumThreat Impact
Identity
Unique IDELEMENT_GLOBAL.2.817747
Element CodeARACF12060
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVertebrate Animal
IUCNLeast concern
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomAnimalia
PhylumCraniata
ClassReptilia
OrderSquamata
FamilyPhrynosomatidae
GenusPhrynosoma
Other Common Names
desert horned lizard (EN)
Concept Reference
Mulcahy, D. G., A. W. Spaulding, J. R. Mendelson, III, and E. D. Brodie, Jr. 2006. Phylogeography of the flat-tailed horned lizard (Phrynosoma mcallii) and systematics of the P. mcallii-platyrhinos mtDNA complex. Molecular Ecology 15(7):1807-1826.
Taxonomic Comments
Phylogenetic analysis of mtDNA sequences by Mulcahy et al. (2006; see also Jezkova et al. 2016) raised the possibility that lizards currently assigned to this species from the Yuma Proving Ground (southwestern Arizona) represent a separate, unnamed species; however, that possibility is contradicted by the results of Farleigh et al. (2021) (Nicholson 2025).

Farleigh et al. (2021) presented evidence from phylogeographic analyses of nuclear SNP data that P. goodei, previously recognized based on mtDNA phylogeny (Mulcahy et al. 2006), is part of one of three genetic clusters within P. platyrhinos, although they did not propose taxonomic unification (Nicholson 2025).
Conservation Status
Rank Method Rank calculation - Biotics v2
Review Date2023-07-23
Change Date2023-07-23
Edition Date2023-07-23
Edition AuthorsHammerson, G. (2016); rev. R. L. Gundy (2023)
Threat ImpactMedium
Range Extent200,000-2,500,000 square km (about 80,000-1,000,000 square miles)
Number of Occurrences81 - 300
Rank Reasons
Desert horned lizards range from southeastern Oregon and southwestern Iowa in the western United States to Baja California in northwestern Mexico. They are relatively common and populations are stable. There have been modest historical declines. It continues to be threatened by habitat degradation due to livestock grazing, invasive grasses, off-road vehicle use, urbanization, and vehicle strikes.
Range Extent Comments
The range of the desert horned lizard extends from southeastern Oregon, southwestern Idaho, and northern Utah south through eastern and southern California, Nevada, and western Arizona, USA to northeastern Baja California, Mexico (Pianka 1991, Grismer 2002, St. John 2002, Stebbins 2003, Mulcahy et al. 2006). Isolated populations exist in the vicinity of dry lake beds in Lake and Harney counties in Oregon. Records from northeastern Utah are based on old records and may not represent extant (or even historical) populations. The elevational range extends from below sea level in desert sinks to about 1,980 meters (6,500 feet) (Barrows et al. 2020, Linsdale 1940, Stebbins 2003).

Populations south of the Gila River in southwestern Arizona and northwestern Sonora, Mexico (formerly included in P. platyrhinos), are now recognized as a distinct species, Phrynosoma goodei (Mulcahy et al. 2006).
Occurrences Comments
This species is represented by a large number of sites that are well distributed throughout the range extent (GBIF 2023, iNaturalist 2023).
Threat Impact Comments
Climate change is a significant threat. Desert horned lizards are expected to decline as increasing temperatures reduce the number of hours they can tolerate being active to forage (Parlin et al. 2020, Sinervo et al. 2010). This species appears to be inhabiting higher elevations in Joshua Tree National Park than has been previously recorded, possibly in response to more arid conditions (Barrows et al. 2020). This species is locally threatened by urbanization and agriculture. Sullivan et al. (2014) could not find this species in any of the surveyed urban preserves in Phoenix, Arizona despite a congener being present at half of them, although it is unclear if this species was ever present there. Invasive grass species, especially cheatgrass (Bromus tectorum), degrades habitat and can make it unsuitable (Billings 1990, Knapp 1996, Newbold 2005). Wind, solar, and geothermal energy also present threats to the habitat (e.g., http://solareis.anl.gov/maps/alternatives/index.cfm). Use of motorized vehicles in the Great Basin and Mojave deserts are localized threats (Busack and Bury 1974).
Ecology & Habitat

Habitat

This lizard inhabits all sorts of desert shrublands, such as those dominated by sagebrush, shadscale, hopsage, creosotebush, or greasewood, on sandy flats, alluvial fans, washes, or brushy dunes or dune edges (Grismer 2002, St. John 2002, Stebbins 2003). It is most consistently found where areas of bare ground exist among openly spaced shrubs. It occurs where summers are hot and winters are cold or mild; winter temperatures generally are too cold for activity.

In Nevada, P. platyrhinos is common in sandy or gravelly valleys and flat areas throughout most of the state at elevations of 610-1,980 meters (mainly above 1,220 meters) (Linsdale 1940). In Arizona, P. platyrhinos inhabits Sonoran, Mohave, and Great Basin desert scrub communities and the lower reaches of interior chaparral and Great Basin conifer woodland, usually in relatively flat, open, areas with sandy or loamy soil, less frequently on rocky bajadas and foothills (Brennan and Holycross 2006). During periods of inactivity the lizards bury themselves in the soil or occupy existing burrows.

Ecology

Desert horned lizards derive their body heat from the environment, They require warm body temperatures for activity, feeding, digestion, and reproduction, but conditions on the surface can become too warm. Lizards attain suitable body temperatures by basking in the sun, moving within the sun-shade mosaic produced by plants, and by burying in the soil or entering a burrow.

Desert horned lizards avoid predators through crypsis (they are very difficult to see unless in motion) and by rapid running into vegetative cover (e.g., Linsdale 1938). The lizards' head spines may interfere with attempted ingestion (and also likely enhance crypsis). This species does not exhibit the defensive blood squirting mechanism present in some horned lizard species (Middendorf and Sherbrooke 1992, Sherbrooke and Middendorf 2004). Predators include: prairie falcons, loggerhead shrikes, longnose leopard lizards and striped whipsnakes.

Drought

Drought may affect populations of horned lizards and other insectivorous reptiles by causing changes in body condition and survival. For example, Texas horned lizards (Phrynosoma cornutum) appear to be sensitive to climate-associated variations in food supply, and drought may reduce food availability and result in lizard weight losses (Whitford and Bryant (1979). In tree lizards (Urosaurus ornatus), reduced growth rate, body condition, and juvenile survival were associated with drought (Tinkle and Dunham (1983). The snake Coluber constrictor, the diet of which includes many insects, exhibited decreased survival during drought conditions in Utah, and juvenile growth was best in years with relatively high rainfall (Brown and Parker 1984).

Drought may also result in reduced reproduction. Fat bodies in the abdominal cavity provide most of the nutrition for reptilian reproduction. Reduced food supplies may reduce reproductive output due to inadequate fat storage. Periods of drought and food shortage may result in smaller clutch sizes. In southern New Mexico, (Worthington 1982) found that drought may result in a one-egg reduction in the average clutch size of the side-blotched lizard (Uta stansburiana).

The effects of drought on survival and reproduction are manifested in reduced population density. For example, in Texas, tree lizard density declined greatly during periods of drought (Ballinger 1977, 1984), evidently due to effects of reduced food resources (Dunham 1981). In California, western whiptail (Aspidoscelis tigris) populations tended to increase with periods of increased arthropod abundance associated with increased precipitation (Anderson 1994). Similarly, A. tigris density varied with drought conditions in southwestern Texas (Milstead 1965).

Thus it is likely that drought results in reduced density of desert horned lizards through the following scenario: Drought reduces plant productivity (including seed production), which in turn reduces insect populations and horned lizard food resources. Reduced food resources result in reduced horned lizard survival and reproduction, which result in reduced population density. In southern Nevada, Medica et al. (1973) observed substantial variation in P. platyrhinos reproduction. Individual females produced one clutch per year in most years and multiple clutches in one year; no evidence of reproduction was observed in one year. The authors did not attempt to associate these variations with environmental parameters but simply speculated that "these deviations may be intimately associated with various density-dependent regulating mechanisms or with differences in net primary production and availability of food."

Reproduction

This lizard is an egg layer. Females bury eggs in the soil. In southern Nevada, egg deposition occurs April-July (apparently mainly early June). Clutch size averages about 7. Individual females produce one or two clutches per year. Incubation lasts about 50-60 days. Hatchlings appear from mid-July to August in southern Nevada, and as late as mid-September in some areas. Individuals become sexually mature in about 22 months (Tanner and Krogh 1973, Nussbaum et al. 1983). Studies in Nevada indicate that some individuals live 7-8 years, occasionally longer (Medica et al. 1973, Tanner and Krogh 1973).
Terrestrial Habitats
DesertSand/dune
Other Nations (1)
United StatesN5
ProvinceRankNative
IdahoS3Yes
NevadaS4Yes
UtahS4Yes
CaliforniaSNRYes
ArizonaS4Yes
OregonS3Yes
Threat Assessments
ThreatScopeSeverityTiming
1 - Residential & commercial developmentSmall (1-10%)Moderate - slightHigh (continuing)
2 - Agriculture & aquacultureRestricted - smallModerate - slightHigh (continuing)
3 - Energy production & miningSmall (1-10%)Slight or 1-10% pop. declineHigh (continuing)
3.3 - Renewable energySmall (1-10%)Slight or 1-10% pop. declineHigh (continuing)
4 - Transportation & service corridorsRestricted - smallModerate - slightHigh (continuing)
4.1 - Roads & railroadsRestricted - smallModerate - slightHigh (continuing)
8 - Invasive & other problematic species, genes & diseasesRestricted (11-30%)Moderate - slightHigh (continuing)
8.1 - Invasive non-native/alien species/diseasesRestricted (11-30%)Moderate - slightHigh (continuing)
11 - Climate change & severe weatherPervasive (71-100%)UnknownHigh - moderate
11.3 - Temperature extremesPervasive (71-100%)UnknownHigh - moderate

Roadless Areas (69)
Arizona (1)
AreaForestAcres
Burro CanyonKaibab National Forest19,928
California (16)
AreaForestAcres
Benton RangeInyo National Forest9,637
Birch CreekInyo National Forest28,816
Black CanyonInyo National Forest32,421
Boundary Peak (CA)Inyo National Forest210,884
ButtermilkInyo National Forest542
Coyote NorthInyo National Forest11,932
Deep CreekSan Bernardino National Forest23,869
Excelsior (CA)Inyo National Forest45,607
Glass MountainInyo National Forest52,867
HortonInyo National Forest5,717
PaiuteInyo National Forest58,712
ScodiesSequoia National Forest725
Soldier CanyonInyo National Forest40,589
South SierraInyo National Forest41,853
TinemahaInyo National Forest27,060
Wonoga Pk.Inyo National Forest11,272
Nevada (40)
AreaForestAcres
Alta T - WestHumboldt-Toiyabe National Forest3,445
Angel Peak NorthHumboldt-Toiyabe National Forest12,577
Bald Mtn.Humboldt-Toiyabe National Forest41,598
Blade CreekHumboldt-Toiyabe National Forest6,331
Boundary Peak (NV)Inyo National Forest21,851
Bunker HillHumboldt-Toiyabe National Forest27,569
Charleston - Macks CynHumboldt-Toiyabe National Forest11,378
Chineese Camp (NV)Humboldt-Toiyabe National Forest15,207
CottonwoodHumboldt-Toiyabe National Forest18,161
Currant - East SlopeHumboldt-Toiyabe National Forest10,101
Excelsior Mtns.Humboldt-Toiyabe National Forest69,071
Four MileHumboldt-Toiyabe National Forest24,093
Fourmile HillHumboldt-Toiyabe National Forest15,718
Georges CanyonHumboldt-Toiyabe National Forest108,551
Grant - BrunoHumboldt-Toiyabe National Forest4,828
Grant - Lower ScofieldHumboldt-Toiyabe National Forest5,816
Grant - RimrockHumboldt-Toiyabe National Forest4,560
Lovell Summit SouthHumboldt-Toiyabe National Forest28,455
Moriah - Hendrys Ck.Humboldt-Toiyabe National Forest2,345
Moriah - Red LedgeHumboldt-Toiyabe National Forest670
Moriah - Silver CreekHumboldt-Toiyabe National Forest1,582
Mt. EtnaHumboldt-Toiyabe National Forest20,527
North StirlingHumboldt-Toiyabe National Forest1,929
Paradise PeakHumboldt-Toiyabe National Forest18,717
Pine Grove NorthHumboldt-Toiyabe National Forest8,749
Pine Grove SouthHumboldt-Toiyabe National Forest88,945
PotosiHumboldt-Toiyabe National Forest5,145
QuinnHumboldt-Toiyabe National Forest62,459
Red MountainHumboldt-Toiyabe National Forest30,242
Rough CreekHumboldt-Toiyabe National Forest8,476
Snake - Big WashHumboldt-Toiyabe National Forest4,146
South SchellHumboldt-Toiyabe National Forest125,614
Stirling - WheelerHumboldt-Toiyabe National Forest3,044
Table Mtn. - EastHumboldt-Toiyabe National Forest87,789
Toiyabe RangeHumboldt-Toiyabe National Forest99,225
Toquima CaveHumboldt-Toiyabe National Forest43,147
Warm SpringsHumboldt-Toiyabe National Forest29,540
Wellington HillsHumboldt-Toiyabe National Forest21,009
West Walker (NV)Humboldt-Toiyabe National Forest5,683
White Pine SouthHumboldt-Toiyabe National Forest11,562
Oregon (2)
AreaForestAcres
Brattain ButteFremont National Forest5,959
Hanan TrailFremont National Forest8,111
Utah (10)
AreaForestAcres
418022Uinta National Forest17,289
CottonwoodDixie National Forest6,754
MogotsuDixie National Forest16,762
Moody WashDixie National Forest31,835
North HillsDixie National Forest24,480
Oak CreekFishlake National Forest54,053
Pine Valley MountainsDixie National Forest57,673
Signal PeakFishlake National Forest30,889
Stansbury MountainsWasatch-Cache National Forest39,696
Stoddard MountainDixie National Forest13,165
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