Penstemon debilis

O'Kane & J. Anderson

Parachute Penstemon

G1Critically Imperiled Found in 1 roadless area NatureServe Explorer →
G1Critically ImperiledGlobal Rank
HighThreat Impact
Parachute beardtongue (Penstemon debilis). Photo by U.S. Fish & Wildlife Service, Public Domain (U.S. Government Work), via ECOS.
U.S. Fish & Wildlife Service, https://www.usa.gov/government-works
Identity
Unique IDELEMENT_GLOBAL.2.149728
Element CodePDSCR1L7C0
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
Endemicendemic to a single state or province
KingdomPlantae
PhylumAnthophyta
ClassDicotyledoneae
OrderPlantaginales
FamilyPlantaginaceae
GenusPenstemon
Other Common Names
Parachute beardtongue (EN) Parachute Beardtongue (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 Date2022-08-31
Change Date1988-05-02
Edition Date2022-08-31
Edition AuthorsS. Spackman and K. Fayette (1998), rev. L. Oliver (2006), rev. K. Neuhaus, J. Handwerk, and S. Panjabi (2006), rev. J. Handwerk (2009, 2012, 2022)
Threat ImpactHigh
Range Extent100-250 square km (about 40-100 square miles)
Number of Occurrences6 - 20
Rank Reasons
Penstemon debilis is endemic to Garfield County, Colorado, USA. This species is restricted the Mahogany Zone of the Parachute Creek Member of the Green River Formation found on the Roan Plateau within the Piceance Basin. Threats to the species include habitat loss and fragmentation associated with energy development, road maintenance, potential competition from invasive plant species and long term drought.
Range Extent Comments
Penstemon debilis is endemic to Garfield County, Colorado, USA. This species is restricted the Mahogany Zone of the Parachute Creek Member of the Green River Formation found on the Roan Plateau within the Piceance Basin. Estimated range extent in Colorado of 114 square kilometers was calculated in GeoCAT using occurrence data provided by the Colorado Natural Heritage Program (2022).
Occurrences Comments
As of 2022 there are 8 known occurrences documented in the Colorado Natural Heritage Program database. All 8 of the occurrences have been observed within the last 20 years. In addition, there is one presumed extirpated occurrence that was last observed in 2014.
Threat Impact Comments
Threats to the species include the loss and fragmentation of habitats associated with energy development, road maintenance, potential competition from invasive plant species and long term drought (USFWS 2022). Although some mine access roads within occupied habitat have been closed, there remain portions of occurrences that have recently been found along gravel roads and continue to be threatened by road maintenance. Non-native invasive plant species have been observed at several sites and may outcompete P. debilis. Long term drought in the region continues to be a concern, and P. debilis declines have been observed in years of lower than average moisture (Handwerk et al. 2022, USFWS 2020). Both drought and habitat shifting and alteration due to climate change are listed as threats in Appendix A of the Colorado State Wildlife Action Plan (Handwerk et al. 2015).
Ecology & Habitat

Description

Penstemon debilis is a member of the figwort family (Schrophulariaceae). It is an herbaceous perennial which often forms mats or trails where the stems may root at the node. The flowers are white to lavender. There are no basal leaves and the cauline leaves are sessile, opposite, succulent and blue-glaucous (O'Kane and Anderson 1987).

Diagnostic Characteristics

Penstemon debilis is endemic to western Colorado. The only other Penstemon species on the western slope of Colorado that completely lacks aerial stems is P. acaulis var. yampensis. P. acaulis var. yampensis differs from P. debilis in its habitat and its green, non-succulent leaves (Weber and Wittmann 1996). Penstemon caespitosus is also mat forming, but has smaller blue flowers and pubescent leaves (McMullen 1998 personal communication). P. debilis is easily identified by its weak stems, soboliferous habit, succulent, glabrous, and glaucous leaves, and its white to pale lavender corollas (O'Kane and Anderson 1987).

Habitat

This species grows on sparsely vegetated, south-facing, steep, white shale talus of the Parachute Creek Member of the Green River Formation. Soils are a mixture of thin shale fragments and clay (Spackman et al. 1997). Associated species include: Agropyron spicatum, Cercocarpus montanus, Chrysothamnus viscidiflorus, Cymopterus hendersonii, Eriogonum lonchophyllum, Galium coloradoense, Holodiscus dumosus, Machaeranthera grindeliodes, Monardella odoratissima, Astragalus lutosus, Festuca dasyclada, and Thalictrum heliophilum (O'Kane and Anderson 1987).

Ecology

Flowers from mid-June to mid-July (Scheck 1994) and fruits in mid July-August (CNHP 1998).

Amy McMullen at Utah State University is currently researching the biology of P. debilis. The following was compiled from her 1997 field season findings, unless otherwise stated:

According to pollination biology studies conducted in 1997, pollinator rarity, chemical or physical properties of the substrate, or seed predation is not responsible for the restriction of P. debilis populations. Seed predation at the known locations is low. The habitat substrate is unusual, however, there is low survival of seeds in greenhouse conditions, either in shale soil or potting soil. P. debilis requires several months of moist chilling to break dormancy.

Bees are responsible for pollination, with Osmia brevis the primary pollinator. This species is thought to be a ground nester west of the Rocky Mountains. Little is known about the biology of this species, however, it has been documented that this bee is responsible for pollination of two other rare Penstemon species in Colorado (P. harringtonii and P. penlandii). Pollinators are also shared with two associated Penstemon species: P. caespitosus and P. mensarum.

The soils of the five known P. debilis locations are of similar physical characteristics but differ in the soil chemistry and plant tissue levels, especially in concentrations of arsenic and selenium. Of the two largest populations, the site with high concentrations of toxic elements had significantly lower densities between P. debilis plants and other species of neighbors. This may reflect reduced competitive ability or survival rates of P. debilis on a substrate with high levels of arsenic, selenium, and mercury.

Breeding system experiments found low fruit production. It is thought that this may be caused by: fragility of the species to disturbance and handling; need for multiple pollinations over several days to set fruit; or outbreeding depression.

Due to the fact that Penstemon debilis does not have any nearby close relatives, O'Kane and Anderson (1987) hypothesize that it is a relictual species. The isolation provided by barren outcrops of oil shale have allowed the species to persist without competition. P. debilis may be a poor competitor and limited to inhospitable sites through competitive exclusion. This explains the habitat specificity, however, there still appears to be more open potential habitat which is unoccupied. This species does seem to be well adapted to its habitat, producing long rhizomes in response to a shifting substrate.

Reproduction

Penstemon debilis flowers from mid-June to mid-July (Scheck 1994) and fruits in mid July-August (CNHP 1998). The plants are bee pollinated and Osmia brevis is the primary pollinator.
Terrestrial Habitats
BarrensBare rock/talus/scree
Other Nations (1)
United StatesN1
ProvinceRankNative
ColoradoS1Yes
Threat Assessments
ThreatScopeSeverityTiming
3 - Energy production & miningLarge (31-70%)Moderate or 11-30% pop. declineHigh - moderate
3.1 - Oil & gas drillingLarge (31-70%)Moderate or 11-30% pop. declineHigh - moderate
4 - Transportation & service corridorsLarge - restrictedSlight or 1-10% pop. declineHigh - moderate
4.1 - Roads & railroadsLarge - restrictedSlight or 1-10% pop. declineHigh - moderate
8 - Invasive & other problematic species, genes & diseasesRestricted (11-30%)Slight or 1-10% pop. declineHigh (continuing)
8.1 - Invasive non-native/alien species/diseasesRestricted (11-30%)Slight or 1-10% pop. declineHigh (continuing)
11 - Climate change & severe weatherPervasive (71-100%)Serious or 31-70% pop. declineHigh (continuing)
11.2 - DroughtsPervasive (71-100%)Serious or 31-70% pop. declineHigh (continuing)

Plant Characteristics
DurationPERENNIAL
Economic Value (Genus)No
Roadless Areas (1)
South Dakota (1)
AreaForestAcres
Indian CreekBuffalo Gap National Grassland24,666
References (21)
  1. Colorado Natural Heritage Program (CNHP). 2022. Biodiversity Tracking and Conservation System (Biotics 5). Colorado Natural Heritage Program, Colorado State University, Fort Collins.
  2. Dawson, C. 2009. Personal communication with Colorado Natural Heritage Program staff regarding BLM rare plant monitoring in Colorado.
  3. Handwerk, J.E., D.G. Malone, N.C. Swayze and J.P. Smith. 2022. Monitoring Colorado’s SWAP Tier 1 plant species Penstemon debilis, 2021. Colorado Natural Heritage Program, Colorado State University, Fort Collins, Colorado.
  4. Handwerk, J., L. Grunau, and S. Spackman-Panjabi. 2015. Colorado Wildlife Action Plan: 2015 Rare Plant Addendum. Colorado Natural Heritage Program, Colorado State University, Fort Collins, Colorado, USA.
  5. Irelend, T. 2002. Candidate and listing priority assignment form: Penstemon debilis. U.S. Fish and Wildlife Service, Grand Junction, Colorado.
  6. 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.
  7. Kraushaar, J.J., and R.A. Ristinen. 1988. Shale Oil. Pages 69-83 in Energy and Problems of a Technical Society. John Wiley and Sons, New York, New York.
  8. McMullen, A.L. 1998. Factors concerning the conservation of a rare shale endemic plant: the reproductive biology and edaphic characteristics of Penstemon debilis (Scrophulariaceae). Master's thesis, Utah State University, Logan, Utah.
  9. Murray, D.K., and J.D. Haun. 1974. Introduction to the geology of the Peceance Creek Basin and vicinity, Northwestern Colorado. Pages 29-39 in D.K. Murray, editor. Energy resources of the Piceance Creek Basin, Colorado, Twenty-fifth field conference. Rocky Mountain Association of Geologists, Denver, Colorado.
  10. O'Kane, S. L. and J. H. Broderick. 2004. Petition to list Parachute Penstemon (<i>Penstemon debilis)</i> as threateed or endangered, prepare and emergency listing rule, and designate critical habitat under the Endangered Species Act (16 U. S. C. 1531, ET SEQ.)<i> . </i>Center for Native Ecosystems, Denver, CO and Colorado Native Plant Society. Ft. Collins, CO.
  11. O'Kane, S.L., Jr., and J.L. Anderson. 1987. Penstemon debilis (Scrophulariaceae): a new species from Colorado endemic to oil shale. Brittonia 39: 412-416.
  12. Rondeau, R.J., M.B. Wunder, A. Meredith, C.A. Pague, and S. Spackman. 1996. Biological survey of Naval Oil Shale Reserve No. 1 (NOSR-1). Unpublished report for the Department of Energy, Casper, Wyoming by the Colorado Natural Heritage Program, Fort Collins, Colorado.
  13. Rondeau, R., K. Decker, J. Handwerk, J. Siemers, L. Grunau, and C. Pague. 2011. The state of Colorado's biodiversity 2011. Prepared for The Nature Conservancy. Colorado Natural Heritage Program, Colorado State University, Fort Collins, Colorado.
  14. Spackman, S. 1996. Colorado Natural Heritage Program Field Survey for <i>Penstemon debilis</i>.
  15. Spackman, S., B. Jennings, J. Coles, C. Dawson, M. Minton, A. Kratz, and C. Spurrier. 1997. Colorado rare plant field guide. Prepared for Bureau of Land Management, U.S. Forest Service and U.S. Fish and Wildlife Service by Colorado Natural Heritage Program.
  16. Spackman, S., K. Fayette, K. Carsey, and R. Rondeau. 1997. Field survey and protection recommendations for the globally imperiled parachute Penstemon, PENSTEMON DEBILIS. Unpublished report for the Colorado Natural Areas Program, Denver, Colorado by the Colorado Natural Heritage Program, Fort Collins, Colorado.
  17. U.S. Fish and Wildlife Service (USFWS). 1996. Endangered and threatened wildlife and plants; review of plant and animal taxa that are candidates for listing as endangered or threatened species. Federal Register 61(40):7596-7613.
  18. U.S. Fish and Wildlife Service (USFWS). 2004. Species assessment and listing priority assignment form. <i>Penstemon debilis.</i> 10 pp.
  19. U.S. Fish and Wildlife Service (USFWS). 2005. Endangered and threatened wildlife and plants; reivew of native species that are canddates or proposed for listing as endangered or threatened; annual notice of findings on resubmitted petitions; annual description of progress on listing actions; proposed rule. Federal Register 70(90):24883.
  20. U.S. Fish and Wildlife Service (USFWS). 2020. Species Status Assessment for Parachute beardtongue (Penstemon debilis). Western Colorado Ecological Services Field Office. Grand Junction, Colorado. Online https://ecos.fws.gov/ecp/species/7099#ssa (Accessed 2022).
  21. U.S. Fish and Wildlife Service (USFWS). 2022. U.S. Fish and Wildlife Service. 2022. Recovery plan for Parachute Beardtongue (Penstemon debilis). August 2022. U.S. Fish and Wildlife Service, Mountain-Prairie Region, Denver, Colorado. 21 pages. Online: https://ecos.fws.gov/docs/recovery_plan/20220817_FinalRecoveryPlan_ParachuteBeardtongue_v5_Signed.pdf (Accessed 2022).