Astragalus tricarinatus

A. Gray

Triple-rib Milkvetch

G2Imperiled Found in 2 roadless areas NatureServe Explorer →
G2ImperiledGlobal Rank
HighThreat Impact
Identity
Unique IDELEMENT_GLOBAL.2.157476
Element CodePDFAB0F920
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
Endemicendemic to a single state or province
KingdomPlantae
PhylumAnthophyta
ClassDicotyledoneae
OrderFabales
FamilyFabaceae
GenusAstragalus
Other Common Names
Triple-ribbed Milk-vetch (EN) triplerib milkvetch (EN)
Concept Reference
Kartesz, 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 Date2021-10-20
Change Date2016-05-17
Edition Date2021-10-19
Edition AuthorsBittman, R.L., rev. C. Russell, rev. Bittman and Treher (2016), Treher (2021)
Threat ImpactHigh
Range Extent1000-5000 square km (about 400-2000 square miles)
Number of Occurrences21 - 80
Rank Reasons
Astragalus tricarinatus is endemic to a small area of California, U.S.A., in Riverside and San Bernardino counties, that occurs in the mountains and canyons bordering the Coachella Valley. Most occurrences are in the foothills of the San Bernardino and Little San Bernardino Mountains. There are several occurrences in the Santa Rosa Mountains. Historically, the species was documented in the Orocopia Range and Chuckwalla Mountains but recent surveys could not relocate plants. The primary threats to this species are illegal off road vehicle use, fire suppression measures and fire, climate change, and invasive plant species. This species is especially vulnerable as most occurrences have less than 15 plants and high rates of mortality have been observed in some areas. There is potential suitable habitat in the vicinity of historical and extant locations that should be surveyed, focusing on areas with Precambrian gneiss.
Range Extent Comments
Astragalus tricarinatus is endemic to a small area of California, U.S.A., in Riverside and San Bernardino counties. The species occurs in the mountains and canyons bordering the Coachella Valley, with most of the occurrences in the foothills of the San Bernardino and Little San Bernardino Mountains. There are three disjunct areas of occurrence in Riverside County in the Agua Alta Canyon in the Santa Rosa Mountains, and the Orocopia Range and Chuckwalla Mountains (Bell and Fraga 2021).
Occurrences Comments
This species is currently known from about 53 occurrences but eight are considered historical because plants haven't been reported from those sites for over 20 years (CNDDB 2021, NatureServe 2021). Surveys in the Orocopia Range and Chuckwalla Mountains failed to relocated historical occurrences but did identify suitable habitat that should be surveyed. The same survey effort confirmed the species is extant in the Santa Rosa Mountains, where it was previously documented by historical occurrences alone (Bell and Fraga 2021).
Threat Impact Comments
This species is threatened by invasive species, illegal off road vehicle use, fire and fire suppression activities, and climate change (Bell and Fraga 2021, USFWS 2009). Expanding residential development near occurrences may increase illegal off road vehicle use activity, foot traffic, and exposure to exotic invasive species (Fraga et al. 2015, USFWS 2009). Sites in the Big Morongo Canyon are potentially threatened by maintenance activities for the crude oil pipeline which runs through its habitat at Big Morongo Canyon (CNPS 2001). The limited number of individuals make it especially vulnerable to unanticipated events, such as pipeline leaks, breaks, or emergency repairs (Fish and Wildlife Service 1998) but also rangewide threats like climate change. As an edaphically restricted species with small population sizes, it may not have sufficient adaptive capacity for a changing climate. Some occurrences may have been impacted by fire but the species response to fire is unknown. Fire suppression activities (bulldozer lines, use of fire retardant) may degrade habitat or create favorable conditions for the spread of non-native invasive plants (USFWS 2009).
Ecology & Habitat

Diagnostic Characteristics

Gynophore 1-2.5 mm long, often hidden within calyx; corolla white to pale cream; pods 25-42 mm long; leaflets retuse. (Barneby in Shreve and Wiggins, 1964)

Habitat

This species occurs on slides, rocky slopes, ledges, and upland ridges with granite or decomposed granite, or carbonate substrates but is also found growing in wash sites that are colonized with seeds that transport from upland areas. The wash sites have very few plants with high rates of mortality and may be described as transient or "waifs" (Bell and Fraga 2021, Fraga et al. 2015).
Terrestrial Habitats
Desert
Other Nations (1)
United StatesN2
ProvinceRankNative
CaliforniaS2Yes
Threat Assessments
ThreatScopeSeverityTiming
4 - Transportation & service corridorsRestricted (11-30%)Serious or 31-70% pop. declineHigh (continuing)
4.2 - Utility & service linesRestricted (11-30%)Serious or 31-70% pop. declineHigh (continuing)
6 - Human intrusions & disturbanceSmall (1-10%)Extreme or 71-100% pop. declineHigh (continuing)
6.1 - Recreational activitiesSmall (1-10%)Extreme or 71-100% pop. declineHigh (continuing)
7 - Natural system modificationsLarge (31-70%)Serious - moderateModerate (short-term)
7.1 - Fire & fire suppressionLarge (31-70%)Serious - moderateModerate (short-term)
7.1.1 - Increase in fire frequency/intensityLarge - restrictedUnknownModerate (short-term)
7.1.2 - Suppression in fire frequency/intensityLarge (31-70%)Serious - moderateHigh (continuing)
8 - Invasive & other problematic species, genes & diseasesLarge (31-70%)UnknownHigh (continuing)
8.1 - Invasive non-native/alien species/diseasesLarge (31-70%)UnknownHigh (continuing)
11 - Climate change & severe weatherPervasive (71-100%)UnknownModerate - low

Plant Characteristics
DurationPERENNIAL, Short-lived
Economic Value (Genus)Yes
Roadless Areas (2)
California (2)
AreaForestAcres
Heartbreak RidgeSan Bernardino National Forest4,455
SugarloafSan Bernardino National Forest8,206
References (10)
  1. Abrams, L. 1944. Illustrated flora of the Pacific states: Washington, Oregon, and California. Vol. 2. Polygonaceae to Krameriaceae. Stanford Univ. Press, Stanford, California. 635 pp.
  2. Bell, D. S., and N.S. Fraga. 2021. Newly Discovered Populations of <i>Astragalus tricarinatus</i> (Triple-Ribbed Milkvetch, Fabaceae) Are Found On Carbonate Soils In the Santa Rosa Mountains, Riverside County, California. Madron~o 67(4):211-217.
  3. California Department of Fish and Game. 2000. Natural Diversity Database (RareFind 2), Version 2.1.2, January 25, 2000. Downloaded in 2003.
  4. California Native Plant Society (CNPS). 2001. Inventory of Rare and Endangered Plants of California (sixth edition). Rare Plant Scientific Advisory Committee, David P. Tibor, Convening Editor. California Native Plant Society. Sacramento, CA. x + 388pp.
  5. California Natural Diversity Database (CNDDB). 2021. RareFind Version 5.2.14. California Department of Fish and Game, Sacramento.
  6. Fraga, N.S., T. Ladoux, L. Prince, M. Harding, AND J. Hoines. 2015. Conservation assessment for Tripleribbed Milkvetch (<i>Astragalus tricarinatus</i>, Fabaceae) in Joshua Tree National Park. Natural Resource Report NPS/JOTR/NRR-2015/999. National Park Service, Fort Collins, CO.
  7. Kartesz, 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.
  8. NatureServe. 2021. NatureServe Network Biodiversity Location Data. NatureServe, Arlington, Virginia.
  9. Shreve, F., and I.L. Wiggins. 1964. Vegetation and flora of the Sonoran Desert. 2 volumes. Stanford Univ. Press, Stanford. 1740 pp.
  10. U.S. Fish and Wildlife Service (USFWS). 1992. Proposed rule for seven desert milk-vetch taxa from California and Nevada. Federal Register 57(90): 19844-19851.