G.W. Douglas & Packer
Identity
Unique IDELEMENT_GLOBAL.2.145524
Element CodePDAST3M4U0
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomPlantae
PhylumAnthophyta
ClassDicotyledoneae
OrderAsterales
FamilyAsteraceae
GenusErigeron
Other Common NamesSalish fleabane (EN) Vergerette de Salish (FR)
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 CommentsFurther taxonomic study appears needed to identify characters that clearly distinguish this species from E. compositus (particularly from the formerly-recognized varieties E. compositus var. glabratus and E. compositus var. discoideus), at least in Washington (J. Arnett pers. comm. 2009).
Conservation Status
Rank Method Rank calculation - Biotics v2
Review Date2025-01-13
Change Date2009-01-26
Edition Date2025-01-13
Edition AuthorsMaybury, K./Douglas, G., rev. K. Gravuer (2009), rev. Johnson, J. (2025)
Threat ImpactMedium
Range Extent20,000-200,000 square km (about 8000-80,000 square miles)
Number of Occurrences6 - 20
Rank ReasonsErigeron salishii is restricted to the highest elevations in a small geographic area - Vancouver Island, British Columbia, and north-central Washington state. Approximately 25 occurrences are currently believed extant; abundant potential habitat is present, so additional occurrences may yet be found. A taxonomic study would allow greater certainty regarding the identity of several Washington occurrences. Immediate threats appear minimal; however, because this species is restricted to high-elevation areas, climate change is likely to pose a significant threat in the future.
Range Extent CommentsErigeron salishii is known from central Vancouver Island, British Columbia, Canada, and from north-central Washington state (Okanogan, Chelan, Kittitas, Skagit, and Snohomish counties), United States. Range extent was estimated using herbarium specimens, photo-based observations, and NatureServe Network occurrence data collected between 1994 and 2025 (GBIF 2025, CPNWH 2025, iNaturalist 2025, NatureServe 2025, SEINet 2025).
Occurrences CommentsIn British Columbia, eleven occurrences are known and others are expected based on abundant potential habitat (J. Penny, pers. comm. 2009, iNaturalist 2025, CPNWH 2025). In Washington, fourteen occurrences are presumed extant and five are believed historical (last observed 1924-1948)(CPNWH 2025, NatureServe 2025, SEINet 2025). By 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 25 occurrences rangewide (GBIF 2025, CPNWH 2025, iNaturalist 2025, NatureServe 2025, SEINet 2025).
Threat Impact CommentsImmediate threats appear minimal in both Washington and British Columbia. Recreational hiking trails may impact a small number of plants. Because this species is restricted to high-elevation areas, however, climate change is likely to pose a significant threat in the future.