Identity
Unique IDELEMENT_GLOBAL.2.146596
Element CodePPSEL011A0
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
Endemicendemic to a single nation
KingdomPlantae
PhylumLycophyta
ClassIsoetopsida
OrderSelaginellales
FamilySelaginellaceae
GenusSelaginella
SynonymsBryodesma utahense(Flowers) Skoda & Holub
Concept ReferenceKartesz, J.T. 1994. A synonymized checklist of the vascular flora of the United States, Canada, and Greenland. 2nd edition. 2 vols. Timber Press, Portland, OR.
Taxonomic CommentsFNA (1993, vol. 2) and the Pteridophyte Phylogeny Group I (2016) recognize the family Selaginellaceae with a single genus, Selaginella. Attempts to recognize subgenera (e.g., six in Zhou and Zhang 2015, seven in Weststrand and Korall 2016) lack consistency, and the elevation of subgenera to nineteen genera in Zhou and Zhang (2023) has mixed acceptance. While Weakley and the Southeastern Flora Team (2025) treat their fifteen taxa in four genera, Valdespino et al. (2024) provide justification to conserve Selaginellaceae in a single genus with approximately 750 taxa, which the World Flora Online (2025) accepts, following the Pteridophyte Phylogeny Group.
Selaginella utahensis is closely related to S. leucobryoides, with small differences in the leaf morphology. Their ranges also overlap and Flora North America vol. 2 (1993) authors also say that not only do their ranges overlap but the morphologic expressions do as well. More study is needed to determine if these are indeed separate species or should be considered one.
Conservation Status
Rank Method Rank calculation - Biotics v2
Review Date2025-05-05
Change Date2025-05-05
Edition Date2025-05-05
Edition AuthorsRoth, E., D. Atwood, rev. J. Morefield, rev. B. Franklin (1996), rev. L. Oliver (2012), rev. N. Ventrella (2025)
Threat ImpactUnknown
Range Extent1000-5000 square km (about 400-2000 square miles)
Number of Occurrences6 - 20
Rank ReasonsSelaginella utahensis is a perennial spikemoss occurring in dry sandstone crevices and protected ledges in sagebrush, oakbrush, pinyon-juniper, and ponderosa pine communities of the western United States, where it is found in Clark County, Nevada, and Kane and Washington counties of Utah. There are an estimated twenty occurrences of this species, with most occurring on protected lands within Zion National Park in Utah. Threats to Selaginella utahensis are largely unknown, but may include recreational impacts and climate change. Selaginella utahensis overlaps in range and characteristics with the closely-related S. leucobryoides and may not be distinct; further research is needed.
Range Extent CommentsSelaginella utahensis occurs in the western United States, in Clark County, Nevada and Kane and Washington counties, Utah (FNA 1993, Welsh et al. 2015). In Nevada, Selaginella utahensis was known historically from southern parts of the state in the Spring Mountains region (Kartesz 1988). A collection from 2005 also confirms this species in the Rainbow Mountain Wilderness region to the west of Las Vegas (John C. Brinda 115 (MO)) (SEINet 2025). An unconfirmed specimen from outside of the known range of this species in Salt Lake County (L.Shultz 19701 (USU)) was omitted from calculations. Range extent was estimated using data from the Utah Rare Plant Database, herbarium specimens, photo-based observations, and NatureServe Network occurrence data collected between 1994 and 2025 (UNHP 2021, GBIF 2025, iNaturalist 2025, NatureServe 2025, RARECAT 2025, SEINet 2025).
Occurrences CommentsBy applying a 1 km separation distance to data from the Utah Rare Plant Database, herbarium specimens, photo-based observations, and NatureServe Network occurrence data documented between 1994 and 2025, it is estimated that there are 20 occurrences rangewide (UNHP 2021, GBIF 2025, iNaturalist 2025, NatureServe 2025, RARECAT 2025, SEINet 2025).
Threat Impact CommentsThreats to Selaginella utahensis are not well documented. In Zion National Park, threats are presumed to be low and populations stable (Alexander 2016), though recreational impacts are possible. Because this species occurs on cliffs, it could be also vulnerable to decreased moisture availability and other microhabitat changes as a result of climate change.