Identity
Unique IDELEMENT_GLOBAL.2.130516
Element CodePDFAB0F6P0
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
Endemicendemic to a single nation
KingdomPlantae
PhylumAnthophyta
ClassDicotyledoneae
OrderFabales
FamilyFabaceae
GenusAstragalus
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.
Conservation Status
Rank Method Rank calculation - Biotics v2
Review Date2025-04-18
Change Date1995-05-30
Edition Date2025-04-18
Edition AuthorsStoner, N. (1993), rev. Johnson, J. (2025)
Threat ImpactMedium
Range Extent20,000-200,000 square km (about 8000-80,000 square miles)
Number of Occurrences21 - 80
Rank ReasonsAstragalus paysonii is a perennial herb that is found in the western United States in western Wyoming and central Idaho. Despite its limited distribution, occurrences are moderately abundant and some occupy large areas. Due to its preference for disturbed habitats, threats to the species are not well understood.
Range Extent CommentsAstragalus paysonii has a limited, split distribution with one group of occurrences in western Wyoming and another in central Idaho (FNA 2023, BONAP 2015). Range extent was estimated using herbarium specimens, photo-based observations, and NatureServe Network occurrence data collected between 1994 and 2025 (GBIF 2025, iNaturalist 2025, NatureServe 2025, RARECAT 2025, SEINet 2025, CPNWH 2025).
Occurrences CommentsBy applying a 1 km separation distance to herbarium specimens, photo-based observations, and NatureServe Network occurrence data documented between 1994 and 2025, it is estimated that there are 76 occurrences rangewide (GBIF 2025, iNaturalist 2025, NatureServe 2025, RARECAT 2025, SEINet 2025, CPNWH 2025).
Threat Impact CommentsAstragalus paysonii is known to prefer open, disturbed sites such as fire scars, clearcuts, utility corridors, and road shoulders (FNA 2023). This species colonizes disturbed areas and gradually declines as competition increases (Heidel 2013). Road maintenance, including mowing and grading, may maintain suitable habitat for this species, but major construction and earth-moving may cause the extirpation of occupied sites (Heidel 2013). Invasive weeds and efforts to control them, may limit the available habitat for this species in disturbed areas.