J.T. Howell
Identity
Unique IDELEMENT_GLOBAL.2.131813
Element CodePMCYP03CQ0
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
Endemicendemic to a single nation
KingdomPlantae
PhylumAnthophyta
ClassMonocotyledoneae
OrderCyperales
FamilyCyperaceae
GenusCarex
Other Common NamesNavajo sedge (EN)
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 CommentsAnalysis of newly collected specimens by Reznicek and Murray (2013) find Carex specuicola to be supported as a distinct species, as recognized by Murray in FNA (2002, vol. 23) and in Kartesz (1994, 1999).
Conservation Status
Rank Method Rank calculation - Biotics v2
Review Date2023-02-09
Change Date2023-02-09
Edition Date2022-09-09
Edition AuthorsRoth, E., rev. Schwartz/Maybury (1996), rev. Treher (2022)
Threat ImpactVery high - high
Range Extent5000-20,000 square km (about 2000-8000 square miles)
Number of Occurrences21 - 300
Rank ReasonsCarex specuicola is a perennial sedge of the western United States that is endemic to Arizona and Utah and primarily occurs on lands managed by the Navajo Nation. It is restricted to hanging gardens, a seepage habitat that relies upon perched aquifers. The greatest threat to this species is aquifer depletion due to long-term drought related to climate change. Some occurrences might be threatened by invasive species, but more monitoring may be needed to understand this potential threat. Many occurrences are on cliffs which protects them from grazing and water diversion.
Range Extent CommentsCarex specuicola occurs in the southwestern United States, where it occurs in Arizona in Coconino, Apache and Navajo counties and Utah in San Juan County. Range Extent was estimated at roughly 19,000 sq km using a minimum convex hull polygon drawn around occurrences (NatureServe 2022, SEINet 2022).
Occurrences CommentsUsing a 1 km separation distance, there are 64 occurrences (USFWS 2019) composed of 160 sites. Due to our limited understanding of population dynamics, the rhizomatous nature of the plants, and the isolated nature of each hanging garden , it may be more appropriate to delineate by hanging garden instead of a standard distance, which would equate to over 160 occurrences (G. Rink, pers. comm., 2022, USFWS 2019).
Threat Impact CommentsThe greatest threat to this species is aquifer depletion due to long-term drought related to climate change. Livestock are present at around six sites but are not documented to cause plant mortality, only damage (USFWS 2019), and that damage has been shown to not be long-term. The interpretation of the threat of livestock was largely eliminated. At one site with extreme grazing, plants have recovered (Rink and Hazelton 2014). Invasive species, including Phragmites australis, are documented at some sites and might pose a threat, but monitoring is needed to determine if those possible threats exist (Nora Talkington, pers. comm., 2022). Plants are often on cliffs where they are protected from livestock (G. Rink, pers. comm. 2022, Nora Talkington, pers. comm., 2022).