Packera malmstenii

(Blake ex Tidestrom) Kartesz

Podunk Groundsel

G3Vulnerable Found in 1 roadless area NatureServe Explorer →
G3VulnerableGlobal Rank
LowThreat Impact
Identity
Unique IDELEMENT_GLOBAL.2.140963
Element CodePDAST8H450
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
Endemicendemic to a single state or province
KingdomPlantae
PhylumAnthophyta
ClassDicotyledoneae
OrderAsterales
FamilyAsteraceae
GenusPackera
Synonyms
Senecio malmsteniiBlake ex Tidestr.
Other Common Names
Podunk Ragwort (EN)
Concept Reference
Kartesz, J.T. 1999. A synonymized checklist and atlas with biological attributes for the vascular flora of the United States, Canada, and Greenland. First edition. In: Kartesz, J.T., and C.A. Meacham. Synthesis of the North American Flora, Version 1.0. North Carolina Botanical Garden, Chapel Hill, N.C.
Taxonomic Comments
Welsh et al. (1987) included the older synonym Senecio malmstenii as within S. streptanthifolius. Kartesz (1994) did not treat S. malmstenii (as recognized or in synonymy), but later accepted Packera malmstenii (Kartesz 1999). Flora of North America (2006) shows Packera malmstenii occurring in Nevada and Idaho, but we follow Kartesz (1999) and Welsh et al. (1993, 2008, 2015) in considering this species to be a southwest Utah endemic, which "is probably more closely allied to S. werneriifolius".
Conservation Status
Rank Method Rank calculation - Biotics v2
Review Date2023-01-19
Change Date2023-01-19
Edition Date2023-01-18
Edition AuthorsGravuer, K. (2009), rev. C. Nordman (2023).
Threat ImpactLow
Range Extent1000-5000 square km (about 400-2000 square miles)
Number of Occurrences6 - 20
Rank Reasons
Podunk Groundsel is endemic to the Tertiary Claron Limestone Formation in Garfield, Kane, and Iron counties, in southwestern Utah, it occurs on the Markagunt and Paunsaugunt Plateaus, Canaan Peak, and the Table Cliff and Aquarius Plateaus. The range extent is estimated to be 2,800 square kilometers, there are about 14 occurrences, plus some additional known occurrences which have not been verified in recent years. Some new occurrences may yet be discovered within the restricted rocky habitat of Podunk Groundsel. Most known occurrences are within the Dixie National Forest, including within the Ashdown Gorge Wilderness Area, it also occurs within the Cedar Breaks National Monument. The total population is estimated to be about 20,000 plants. Threat impacts to it from recreation are low because of its largely inaccessible habitat. The high calcium carbonate content of its rocky habitat restricts the establishment of invasive plants.
Range Extent Comments
Podunk Groundsel occurs in the western United States, it is endemic to only three counties in southwestern Utah, the range extent is estimated to be 2,800 square kilometers. It occurs on Tertiary Claron Limestone Formation of the Markagunt and Paunsaugunt Plateaus, in locations such as the Ashdown Gorge Wilderness and Cedar Breaks National Monument (Iron County) and just outside southwest corner of Bryce Canyon National Park (Kane County), and on Canaan Peak and Table Cliff Plateau (including Barney Top and Horse Creek Top) to Aquarius Plateau (including south end of Boulder Mountain) (Garfield County). Populations are fairly scattered, within 60-70 air miles of each other (M. Madsen pers. comm. 2009, NatureServe 2023, SEINet 2023, Utah Natural Heritage Program 2021, Welsh et al. 2015).
Occurrences Comments
Field survey for Podunk Groundsel by M. Madsen in the Dixie National Forest (mostly 2000, 2004, 2020) and a survey of the Cedar Breaks National Monument by W. Fertig and D. Reynolds (2007-2008) bring the total number of known occurrences to approximately 19, 14 of which have been observed since 1999 (M. Madsen pers. comm. 2009, SEINet 2023, W. Fertig pers. comm 2009). Additional occurrences may yet be discovered, as the plant is small and easily overlooked, and it occurs in many remote and/or very difficult to access areas (W. Fertig pers. comm. 2009). Although apparently not confirmed within the boundaries of Bryce Canyon National Park, it likely occurs there (M. Madsen pers. comm. 2009).
Threat Impact Comments
Threats to Podunk Groundsel are low, they are limited due to its inaccessible habitat (Alexander 2016, W. Fertig pers. comm. 2009, M. Madsen pers. comm. 2009). One occurrence is near a trail to a scenic point, but most trails are not close to Podunk Groundsel populations because its steep, erodible habitat is not suitable for trail routing and construction (M. Madsen pers. comm. 2009). Approximately 12% of occupied and potentially suitable habitat for Podunk Groundsel within the Dixie National Forest is within 500 feet of routes open to motorized vehicle access (Madsen 2009), but impacts from vehicles are unlikely due to the low accessibility of sites. Rodriguez (2004) states that "this species is not affected by grazing because plants are generally on steep Claron limestone talus slopes where grazing does not occur." There have not been issues in the past with invasive species because the high calcium carbonate content of this species' preferred substrate creates harsh abiotic conditions in which only specifically-adapted plants can succeed (M. Madsen pers. comm. 2009). Podunk Groundsel may be threatened by extreme or exceptional drought, which may become more common with climate change (W. Fertig pers. comm. 2009).
Ecology & Habitat

Description

A smooth perennial herb that is soboliferous (with slender rhizomes to 20 cm or longer connecting the buried upslope caudex to the year's stems); each year, the stems arise from the ends of the sobols. Plants are typically 4.5-7 cm tall above ground, with above-ground stems more or less upright. Leaves (essentially all basal) are thick, stalked, and round to egg-shaped with the widest part at the top; they are 1-3 cm long and are either unlobed or have a few, regular lobes. There are 1-2 flower heads per plant. The involucre is 7-10 mm high with 12-16 suffused purple, narrowly lance-subulate flower bracts. All flowers in the head are discoid (no ray flowers) and are yellow to orangish. The pappus is white with smooth bristles and the achene is smooth (Rodriguez 2004, Utah Native Plant Society 2008, Fertig and Reynolds 2009).

Diagnostic Characteristics

Distinguished from S. werneriifolius primarily by its lack of ray flowers, and also by its thinner sobols (1mm thick vs. 2-3 mm thick in S. werneriifolius) and glabrous foliage (the pubescence of S. werneriifolius varies from copious to almost none, but there is usually a hint of pubescence) (Welsh et al. 2008). Distinguished from Senecio musiniensis and S. castoreus by its glabrous foliage; these other species are grayish to white woolly pubescent (Fertig and Reynolds 2009). Other co-occurring Senecio species differ in having yellow ray flowers, taller and leafier stems, tomentose herbage, or leaf blades that are either narrower or pinnately lobed (Fertig and Reynolds 2009). Distinguished from Senecio soldanella and Senecio (Packera) porteri of adjacent Colorado by its smaller flower heads.

Habitat

Podunk Groundsel is associated with spruce-fir and mixed conifer forests on talus slopes of Tertiary Claron Limestone Formation (Welsh et al 2015). It occurs at high elevations primarily on steep creeping talus slopes (also eroding outcrops and cliff edges) of the Tertiary Claron (also known as Wasatch) Limestone Formation, an Eocene-age sandy limestone derived from an ancient deep lake. Few other plants typically establish in these habitats, due to the high pH and erodibility of the rock, the fact that slopes are underlain by thick clay that is very hard when dry, and the exposure of sites to the elements (strong winds, intense sunlight, blowing snow, freeze-thaw cycles, intense thunderstorms). The special soil conditions (particularly the high pH) have resulted in several endemic plants (W. Fertig pers. comm. 2009). This species' soboliferous habit appears to be an adaptation to mantle-creep of the limestone slopes (Welsh et al. 2008). In the Cedar Breaks area, populations are often found associated with shallow erosional channels or rills that run parallel to the slope axis and expose bare, clayey soil (Fertig and Reynolds 2009). The immediate community typically has very low vegetation cover (averaging less than 10%, often 1-2%), and has been described as "barrens" and as a "cushion-plant community." The surrounding community is conifer woodland (western bristlecone pine, western bristlecone pine-limber pine, spruce-fir, western bristlecone pine-douglas fir, mixed conifer); sometimes some of these trees manage to establish on the slopes. Associated species include Cymopterus minimus, Silene petersonii, Senecio atratus, Astragalus miser var. oblongifolius, Eriogonum panguicense var. alpestre, Haplopappus zionis, Calamagrostis scopulorum, and Monardella odoratissima. 2250-3200 m (Fertig and Reynolds 2009, W. Fertig pers. comm. 2009).
Terrestrial Habitats
Forest/WoodlandWoodland - ConiferBarrensBare rock/talus/scree
Other Nations (1)
United StatesN3
ProvinceRankNative
UtahS3Yes
Threat Assessments
ThreatScopeSeverityTiming
6 - Human intrusions & disturbanceRestricted (11-30%)Slight or 1-10% pop. declineHigh (continuing)
6.1 - Recreational activitiesRestricted (11-30%)Slight or 1-10% pop. declineHigh (continuing)

Plant Characteristics
DurationPERENNIAL
Economic Value (Genus)No
Roadless Areas (1)
Utah (1)
AreaForestAcres
Lava BedsDixie National Forest14,944
References (20)
  1. Alexander, J. 2016. The Utah Native Plant Society Rare Plant List: Version 2. Calochortiana. 3: 1-248.
  2. Fertig, W. 2009. Annotated checklist of vascular flora: Cedar Breaks National Monument. Natural Resource Technical Report NPS/NCPN/NRTR-2009/173. National Park Service, Fort Collins, Colorado. [http://science.nature.nps.gov/im/units/ncpn/Bib_Library/inventory/CEBR_Flora_Report_2009.pdf]
  3. Fertig, Walter. Personal communication. Moenave Botanical Consulting, Kanab, Utah.
  4. Fertig, W. and D. N. Reynolds. 2009. Survey of Rare Plants of Cedar Breaks National Monument: Final Report CPCESU Cooperative Agreement # H1200-004-0002 Survey Rare Plants and Establish Compliance with Conservation Agreement for Arizona Willow at Cedar Breaks National Monument. Prepared for Cedar Breaks National Monument, The Colorado Plateau Cooperative Ecosystem Studies Unit, and Southern Utah University. 20 January 2009.
  5. Flora of North America Editorial Committee (FNA). 2006b. Flora of North America north of Mexico. Vol. 20. Magnoliophyta: Asteridae, part 7: Asteraceae, part 2. Oxford Univ. Press, New York. xxii + 666 pp.
  6. Kartesz, J.T. 1999. A synonymized checklist and atlas with biological attributes for the vascular flora of the United States, Canada, and Greenland. First edition. In: Kartesz, J.T., and C.A. Meacham. Synthesis of the North American Flora, Version 1.0. North Carolina Botanical Garden, Chapel Hill, N.C.
  7. Madsen, Mark T. Personal communication. Botanist, Dixie National Forest, Utah.
  8. Madsen, M. T. 2009. Biological Evaluation of Sensitive Plant Species for the Motorized Travel Plan Project Preferred Alternative with Modifications. Dixie National Forest. [http://www.fs.fed.us/r4/dixie/projects/MTP/feis/specialist_reports/plant_be.pdf]
  9. NatureServe. 2023. NatureServe Network Biodiversity Location Data. NatureServe, Arlington, Virginia.
  10. 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]
  11. Smith, L. Y. and B. Monroe. 2008. Rare Plants Specialist Report: Motorized Travel Plan, Dixie National Forest. U.S. Forest Service. May 2008. [www.fs.fed.us/r4/dixie/projects/MTP/deis/specialist_reports/rare_plants.pdf]
  12. Southwest Environmental Information Network (SEINet). 2023. Collections Databases. Online. Available: https://swbiodiversity.org/seinet/collections/index.php (accessed 2023).
  13. U.S. Fish and Wildlife Service (USFWS). 2009. Endangered and Threatened Wildlife and Plants; Partial 90-Day Finding on a Petition To List 206 Species in the Midwest and Western United States as Threatened or Endangered With Critical Habitat. Federal Register 74(23): 6122-6128. 5 February 2009.
  14. U.S. Forest Service (USFS). 2009. Record of Decision for the Dixie National Forest Motorized Travel Plan. U.S. Forest Service, Intermountain Region, Dixie National Forest. April 2009. [www.fs.fed.us/r4/dixie/projects/MTP/feis/mtp_rod_with_maps.pdf]
  15. Utah Native Plant Society. 2003-2008. Utah Rare Plant Guide. Salt Lake City, UT: Utah Rare Plant Guide Home Page. Online. Available: http://www.utahrareplants.org (accessed 2009).
  16. Utah Native Plant Society (UNPS). 2003-2021. Utah rare plant guide. A.J. Frates editor/coordinator. Salt Lake City, UT. Utah Native Plant Society. Online. Available: https://www.utahrareplants.org (accessed 2021).
  17. Utah Natural Heritage Program. 2021. Utah Rare Plant Database (accessed 2021).
  18. 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.
  19. Welsh, S.L., N.D. Atwood, S. Goodrich and L.C. Higgins. (Eds.) 2008. A Utah Flora. 4th edition, revised. Brigham Young University, Provo, Utah, U.S.A. 1019 pp.
  20. 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.