Castilleja parvula

Rydb.

Tushar Indian-paintbrush

G1Critically Imperiled Found in 3 roadless areas NatureServe Explorer →
G1Critically ImperiledGlobal Rank
Very highThreat Impact
Identity
Unique IDELEMENT_GLOBAL.2.151648
Element CodePDSCR0D3K0
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
Endemicendemic to a single state or province
KingdomPlantae
PhylumAnthophyta
ClassDicotyledoneae
OrderScrophulariales
FamilyOrobanchaceae
GenusCastilleja
Synonyms
Castilleja parvula var. parvula
Other Common Names
Tushar Paintbrush (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.
Taxonomic Comments
As treated here (following Kartesz, 1994 checklist), this record excludes Castilleja revealii, sometimes treated as C. parvula var. revealii.
Conservation Status
Rank Method Rank calculation - Biotics v2
Review Date2025-04-23
Change Date2025-04-23
Edition Date2025-04-23
Edition AuthorsB. Franklin & K. Maybury (1992), rev. Treher (2016), rev. M. McCormick (2024) and N. Ventrella (2025)
Threat ImpactVery high
Range Extent<100 square km (less than about 40 square miles)
Number of Occurrences1 - 5
Rank Reasons
Castilleja parvula is a perennial forb occurring on Tertiary igneous gravels from 2,700 to 3,700 m in elevation in the alpine or krummholz zone of the Tushar Mountains, Utah, in Piute and Beaver counties, and as an outlier population in Garfield County. There are an estimated five occurrences of this species located primarily on U.S. Forest Service-administered lands in Dixie and Fishlake National Forests. Threats to Castilleja parvula include grazing-related impacts, particularly from non-native introduced mountain goats, climate change and drought, and recreation. This species requires close monitoring by land managers due to it being highly utilized and preferred by ungulates for forage. Mountain goat herbivory is pushing this species on a trajectory of local extinction in core-use areas, and targeted management of mountain goats is highly recommended, especially in the Mt. Holly region.
Range Extent Comments
Castilleja parvula occurs in the western United States, where it is endemic to upper elevations of the Tushar Mountains, Utah, in Piute and Beaver counties, and as an outlier population in Garfield County (Welsh et al. 2015, Alexander 2016, FNA 2019). Range extent was calculated using data from the Utah Rare Plant Database (2024).
Occurrences Comments
By applying a 2 km separation distance to population location data from the Utah Rare Plant Database, there are five estimated occurrences (2024).
Threat Impact Comments
Threats to Castilleja parvula include grazing-related impacts, climate change and drought, and recreation (UNHP 2024, UNPS 2025). Mountain goats were introduced to the Tushar Mountains in 1986 for the purpose of trophy hunting, and are now naturalized to the region (Taye 1995). Grazing impacts have been observed from mountain goats, trespass cows, and native ungulates like deer, rodents and other lagomorphs. In a study of mountain goat and deer foraging preferences in the Tushars (Shipp 2022), Castilleja parvula was foraged at a significantly higher rate than would be expected based on cover, indicating that it is preferentially grazed by both deer and mountain goats. In four long-term monitoring plots established for this species, 20 to 58 percent of tagged Castilleja parvula showed evidence of herbivory by ungulates. Mountain goat herbivory is particularly heavy on Mt. Holly, where 97.4% of the herbivore captures from game cameras were mountain goats (Allphin 2025). Based on an analyses of fecal DNA samples from cows, mountain goats, pika, marmots, elk, and deer, Allphin (2025) calls this plant an "ice cream species," meaning that everything eats it. While it may have evolved to withstand some level of grazing by native ungulates, it is doubtful that this species can withstand current levels of grazing pressure with the introduction of a non-native species.

Climate change is also a threat likely impacting this species throughout its range (Wrobleski 2023). Droughts and rapid snowmelt due to wind-blown sediments are melting snowpack earlier than normal in this region (UNPS 2025). Recreational use of habitat, such as foot traffic, dispersed camping, and off-road vehicles may pose a threat to some populations, and hiking and off-road vehicle use has been increasing in recent years (Allphin 2025). As the human population grows in areas within easy access to habitat, and as recreational use increases, the impacts may become more significant. Historically, mining claims and exploration have impacted the available habitat, which has potentially contributed to its imperiled status today (Rodriguez 2004).
Ecology & Habitat

Habitat

Castilleja parvula occurs in gravelly meadows, ridgetops, rocky slopes, and talus in the alpine or krummholz zone on Tertiary igneous gravels from 2700 to 3700 m in elevation (FNA 2019). Associated species include Engelmann spruce, Cymopterus, Haplopappus, Monardella, and Ribes (Welsh et al. 2015).

Reproduction

Castilleja parvula produces flowers from June to August, and seeds are dispersed by wind or gravity (Rodriguez 2004). Shipp (2022) recorded an average of 0.53 (±0.02 SE) seed-to-ovule ratio at four monitoring sites established for the species.
Terrestrial Habitats
Alpine
Other Nations (1)
United StatesN1
ProvinceRankNative
UtahS1Yes
Threat Assessments
ThreatScopeSeverityTiming
2 - Agriculture & aquaculturePervasive (71-100%)Moderate - slightHigh (continuing)
2.3 - Livestock farming & ranchingPervasive (71-100%)Moderate - slightHigh (continuing)
2.3.4 - Scale unknown/unrecordedPervasive (71-100%)Moderate - slightHigh (continuing)
3 - Energy production & miningRestricted (11-30%)Serious - moderateInsignificant/negligible or past
3.2 - Mining & quarryingRestricted (11-30%)Serious - moderateInsignificant/negligible or past
6 - Human intrusions & disturbancePervasive (71-100%)Moderate or 11-30% pop. declineHigh (continuing)
6.1 - Recreational activitiesPervasive (71-100%)Moderate or 11-30% pop. declineHigh (continuing)
8 - Invasive & other problematic species, genes & diseasesLarge (31-70%)Extreme or 71-100% pop. declineHigh (continuing)
8.1 - Invasive non-native/alien species/diseasesLarge (31-70%)Extreme or 71-100% pop. declineHigh (continuing)
8.1.2 - Named speciesLarge (31-70%)Extreme or 71-100% pop. declineHigh (continuing)
11 - Climate change & severe weatherPervasive (71-100%)Serious - moderateHigh (continuing)
11.1 - Habitat shifting & alterationPervasive (71-100%)Serious - moderateHigh (continuing)

Plant Characteristics
DurationPERENNIAL
Economic Value (Genus)No
Roadless Areas (3)
Utah (3)
AreaForestAcres
Bullion - DelanoFishlake National Forest14,917
City CreekFishlake National Forest13,939
Tushar MountainFishlake National Forest39,992
References (15)
  1. Alexander, J. 2016. The Utah Native Plant Society Rare Plant List: Version 2. Calochortiana. 3: 1-248.
  2. Allphin, L. 2025. Monitoring of rare plant populations and mountain goat use in the alpine communities of the La Sal and Turshar Mountains. Presentation at the 2025 Wildlife Board Work Session, Utah Department of Natural Resources. Online. Available: <a href="https://www.youtube.com/watch?v=hmK9j1U-9Cw&amp;list=PLWIxD5-tnhxr8SUVBFbo-xbMR_pS5aQ_x&amp;index=2">www.youtube.com/watch?v=hmK9j1U-9Cw&list=PLWIxD5-tnhxr8SUVBFbo-xbMR_pS5aQ_x&index=2</a> (accessed 2025).
  3. Cronquist, A., A.H. Holmgren, N.H. Holmgren, J.L. Reveal, and P.K. Holmgren. 1984. Intermountain Flora: Vascular Plants of the Intermountain West, U.S.A. Vol. 4, Subclass Asteridae (except Asteraceae). New York Botanical Garden, Bronx. 573 pp.
  4. Flora of North America Editorial Committee (FNA). 2019. Flora of North America north of Mexico. Vol. 17: Magnoliophyta: Tetrachondraceae to Orobanchaceae. Oxford Univ. Press, New York. xxiv + 737 pp.
  5. 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.
  6. Reed, Johannah. 2012. The Effects of Hemiparasitism by <i>Castilleja</i> Species on Community Structure in Alpine Ecosystems. Pursuit-The Journal of Undergraduate Research at The University of Tennessee 3(2): 99-109.
  7. Rodriguez, R. L., compiler. 2004. Life History and Analysis of Endangered, Threatened, Candidate, Sensitive, and Management Indicator Species of the Dixie National Forest. Version 4.0, Revised February 2004. [www.fs.fed.us/r4/dixie/publications/02-2004_dixie_life_history_report.pdf]
  8. Shipp, Heather. 2022. Monitoring of foraging sites for ungulates within alpine plant communities and establishment of long-term monitoring plots for rare <i>Castilleja parvula</i> var. <i>parvula</i> in the Tushar Mountains, Utah. M.S. Thesis. Brigham Young University, Provo, UT. 126 pp.
  9. Taye, A. C. 1995. Alpine vascular flora of the Tushar Mountains, Utah. Great Basin Naturalist 55(3): 225-236.
  10. Utah Native Plant Society (UNPS). 2025. 2016-2025 UNPS Utah Rare Plant Master List . Online. Available: www.utahrareplants.org/rpg_species.html (Accessed 2025).
  11. Utah Natural Heritage Program (UNHP). 2024. Element Subnational Ranking Form: <i>Castilleja parvula</i> in Biotics 5 database. NatureServe, Arlington, Virginia (accessed 7 April 2025).
  12. Welsh, S.L. 1979. Illustrated manual of proposed endangered and threatened plants of Utah. Brigham Young Univ., Provo, UT. 318 pp.
  13. Welsh, S.L., N.D. Atwood, S. Goodrich, and L.C. Higgins (eds.) 1993. A Utah flora. 2nd edition. Brigham Young Univ., Provo, Utah. 986 pp.
  14. Welsh, S.L., N.D. Atwood, S. Goodrich, and L.C. Higgins. (Eds). 2015. A Utah flora, fifth edition, revised 2015. Monte L. Bean Life Science Museum, Provo, Utah. 987 pp.
  15. Wrobleski, A., Ernst, S., Weber, T., and A. Delach. 2023. The impact of climate change on endangered plants and lichen. PLOS Climate 2(7): e0000225.