Antennaria arcuata

Cronq.

Meadow Pussytoes

G3Vulnerable Found in 3 roadless areas NatureServe Explorer →
G3VulnerableGlobal Rank
Identity
Unique IDELEMENT_GLOBAL.2.128591
Element CodePDAST0H050
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
Endemicendemic to a single nation
KingdomPlantae
PhylumAnthophyta
ClassDicotyledoneae
OrderAsterales
FamilyAsteraceae
GenusAntennaria
Other Common Names
box pussytoes (EN) Box Pussytoes (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
Distinct, although no studies have been done to show that the Wyoming, Idaho and Nevada (all significantly disjunct) populations represent the same taxon.
Conservation Status
Rank MethodLegacy Rank calculation - Excel v3.1x
Review Date2013-01-02
Change Date2013-01-02
Edition Date2013-01-02
Edition AuthorsMarriott, H. (2/87 and 9/90)(Rev. W. Fertig/K. Maybury 6/96 and 12/97), rev. B. Heidel (1/2013).
Range Extent1000-5000 square km (about 400-2000 square miles)
Number of Occurrences21 - 80
Rank Reasons
Based on 34 extant occurrences (29 in Wyoming), with disjunct occurrences in Idaho and Nevada. The plants are restricted to geographically isolated wet areas, such as those that form around springs and seeps, though hydrology has not been evaluated. This habitat attracts grazing animals, and moderate grazing may be beneficial as it reduces the cover of competing vegetation; the effects of heavy grazing are not known.
Range Extent Comments
Regional endemic found in four disjunct areas in south-central Idaho, northeastern Nevada, central and southwestern Wyoming.
Occurrences Comments
Known from 29 extant occurrences in Wyoming and one possibly extirpated, 4 extant occurrences in Nevada, and 1 in Idaho, for a total of 34 extant occurrences.
Threat Impact Comments
Marriott (1986) identified overgrazing, water development (stockpond construction), placer mining, and uranium mining as potential threats to Antennaria arcuata. Exclosure studies by the BLM suggest that grazing is less of a threat than originally thought, although trampling may still be a concern. Populations of A. arcuata often abruptly stop inside of ungrazed exclosures where graminoid cover is too dense and soils are too moist. Under appropriate stocking levels and rotation, grazing appears to be beneficial to this species by maintaining low cover and moist (but not too wet) soil conditions (Fertig 1996). Off-road vehicle damage, mineral development, and water projects that include both impoundments and stockponds appear to be the primary threats at present in Wyoming. Populations in the Upper Green River Basin may also be threatened by oil and gas development. Competition from exotic weeds has also been cited as a threat in Idaho, and invasion by Cirsium arvense was noted in one Upper Green River Basin population in Wyoming. On private lands, its habitat could be threatened to plowing and reseeding to hayfields. Its habitat may also be vulnerable to dessicating climate conditions.
Ecology & Habitat

Description

Antennaria arcuata is a loosely white-woolly perennial herb with conspicuously arching stolons. Stolons extend up to 1 dm long and give rise to new plants. Plants are dioecious (either staminate or pistillate). Basal leaves are few, wider at the top, and several cm long. Flowering stems are solitary, 3 to 4 dm tall, with well-developed, and gradually reduced stem leaves. The flower heads are moderately numerous and arranged in a close terminal cluster. Male and female plants vary slightly in size of flowers, involucre (bracts at base of flower head), and pappus (modified calyx on top of ovary/fruit) (Lorain 1990).

Diagnostic Characteristics

The most distinctive feature of Antennaria arcuata is its conspicuously arching, woolly stolons (hence its common name). This feature is diagnostic. Other characters to look for are the single flowering stem, white-woolly pubescence, and preference for damp meadow habitats.

Habitat

Moist meadows, often on hummocks of sedges and rushes that stay drier than the surrounding areas, or at the edges of these meadows. 1500-2400 m. The wet meadows are usually surrounded by sagebrush grassland communities.

In Wyoming, Antennaria arcuata is found primarily in subirrigated meadows within broad stream channels dominated by tufted hairgrass (Deschampsia arcuata), Baltic rush (Juncus balticus), Kentucky bluegrass (Poa pratensis), Nevada bluegrass (Poa nevadensis), Junegrass (Koeleria macrantha), and clustered field sedge (Carex praegracilis). These communities are often found in a matrix of silver sagebrush (Artemisia cana) and shrubby cinquefoil (Potentilla fruticosa). Within these communities, A. arcuata is most commonly associated with hummocky topography, but it also occurs on level ground, or shallow depressions. Soils tend to be alkaline, clayey, and high in organic matter. At higher elevations in the South Pass area, it may be found at the edge of silver sagebrush stands and willow thickets in subirrigated meadows of tufted hairgrass, Baltic rush, spike-rush(Eleocharis sp.), and meadow barley (Hordeum brachyantherum). Antennaria arcuata is notably absent from riparian sites with tall, dense graminoid or shrub cover, and where soils are saturated. It is also absent from the dry, gravelly big sagebrush (Artemisia tridentata) grassland ridges bordering the meadow habitats (Fertig 1996).

The one Idaho population occupies a mesic natural grass-sedge meadow surrounded by sagebrush-steppe (Lorain 1990). Nevada populations are found in open, flat meadows that are not permanently wet (Mozingo and Williams 1980).

Ecology

Antennaria arcuata appears to decrease in areas with tall or dense vegetation cover. Colonies within BLM exclosures have declined or been locally extirpated where grazing has been prevented and the vegetation notably denser and taller. High vegetation cover may also promote greater water retention in the soil, creating microsites too wet for A. arcuata. Several Wyoming colonies have also declined over time where shrubs have replaced the graminoid plant community. In Wyoming, A. arcuata is often found with Antennaria microphylla in hummocky habitats. Antennaria microphylla generally replaces A. arcuata on drier hummock tops and on wetter soil sites. Changes in soil moisture retention capacity, either through increased vegetation density or soil compaction, may favor A. microphylla at many sites (Fertig 1996).

Reproduction

Antennaria arcuata is a perennial that reproduces vegetatively by spreading stolons, or sexually by seed. Although many species of Antennaria also reproduce asexually by apomixis (the production of viable seed without fertilization or meiosis), there is no evidence of this in A. arcuata (Bayer 1984). Chromosome counts and demographic analysis of Wyoming and Nevada populations have shown this species to be a diploid, with populations containing approximately equal proportions of staminate and pistillate individuals (Bayer 1992). Mature, presumably viable fruits were commonly observed in Wyoming populations. On average, pistillate plants contained 10-12 heads per flowering stem, and 20 fruits per head (Fertig 1996). The one Idaho population is reported to be comprised of only pistillate plants (Lorain 1990). This needs further investigation. Known apomictic species of Antennaria are polyploids with populations consisting almost entirely of pistillate plants (Bayer 1984).

Bayer (1992) found the amount of genetic diversity within populations of A. arcuata to be much lower than other narrowly endemic, or wide-ranging sexual species of Antennaria. Due to inbreeding within populations and low gene flow between populations, Bayer also reports small, but meaningful differences in the genetic structure of six A. arcuata occurrences in Nevada, Idaho, and Wyoming. These observations support the contention that populations have been isolated from each other for a relatively long time (Bayer 1992).

Possible hybridization or introgression between A. arcuata and A. microphylla has been reported from one Wyoming occurrence (Bayer 1992). Unlike polyploid species in Antennaria, hybridization appears to be uncommon among the diploid taxa of the genus (Cronquist 1994).
Palustrine Habitats
HERBACEOUS WETLAND
Other Nations (1)
United StatesN3
ProvinceRankNative
IdahoS1Yes
NevadaS1Yes
WyomingS3Yes
Plant Characteristics
DurationPERENNIAL
Economic Value (Genus)No
Roadless Areas (3)
Nevada (3)
AreaForestAcres
Copper Mtns.Humboldt-Toiyabe National Forest31,945
Jenneman PeakHumboldt-Toiyabe National Forest6,431
Pine Mtn.Humboldt-Toiyabe National Forest12,519
References (17)
  1. Anderson, S., M. White and D. Atwood. 1991. Humboldt National Forest sensitive plant field guide. U.S. Forest Service Intermountain Region, Ogden, UT. 32 pp.
  2. Atwood, D. 1980. Status report on <i>Antennaria arcuata</i>. USDA Forest Service, Ogden, UT. Not paged.
  3. Bayer, F. J. 1992. Allozyme variation, genecology, and phytogeography of <i>Antennaria arcuata</i> (Asteraceae), a rare species from the Great Basin and Red Desert with small disjunct populations. American Journal of Botany 79(8): 872-881.
  4. Cronquist, A. 1950. Notes on the Compositae of the northwestern U.S. Leaflets of Western Botany 6: 41-50.
  5. Cronquist, A. 1994. Asterales. In A. Cronquist, A.H. Holmgren, N.H. Holmgren, J.L. Reveal, and P.K. Holmgren. Intermountain flora: Vascular plants of the Intermountain West, U.S.A. Vol. 5. New York Botanical Garden, Bronx. 496 pp.
  6. Cronquist, A., A. H. Holmgren, N. H. Holmgren, J. L. Reveal, and P. K. Holmgren. 1994. Intermountain flora: Vascular plants of the Intermountain West, U.S.A., Volume 5. The New York Botanical Garden, Bronx, NY.
  7. Dorn, R.D. 1980. Illustrated guide to special interest vascular plants of Wyoming. U.S. Fish and Wildlife Service and Bur. Land Management, Cheyenne, Wyoming. 67 pp.
  8. Fertig, W. 1996. Status report on Antennaria arcuata in central Wyoming. Unpublished report prepared for the Bur. Land Management, Wyoming State Office, by the Wyoming Natural Diversity Database, Laramie. 126 pp.
  9. Fertig, W., C. Refsdal, and J. Whipple. 1994. Wyoming rare plant field guide. Wyoming Rare Plant Technical Committee, Cheyenne. No pagination.
  10. Heidel, B. 2013. Status of <i>Antennaria arcuata </i>(Meadow pussytoes) in southwestern Wyoming. Prepared for the USDA Bureau of Land Management - Pinedale and Rock Springs Field Offices by the Wyoming Natural Diversity Database - University of Wyoming, Laramie, Wyoming. <br>
  11. 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.
  12. 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.
  13. Lorain, C. C. 1990. Report on the conservation status of <i>Antennaria arcuata</i> in Idaho. Unpublished report prepared for Idaho Department of Parks and Recreation. 42 pp. plus appendices.
  14. Marriott, H. 1986. Status report on Antennaria arcuata. Unpublished report prepared for the U.S. Fish and Wildlife Service by the Wyoming Natural Diversity Database, Laramie, WY. 42 pp. + appendices.
  15. Mozingo, H.N., and M. Williams. 1980. The threatened and endangered plants of Nevada. U.S. Fish and Wildlife Service and Bureau of Land Management, Portland, OR. 268 pp.
  16. Packard, P. L. 1979. Status report for <i>Antennaria arcuata</i>. The College of Idaho, Caldwell. 7 pp.
  17. Steele, B., F. Johnson, and S. Brunsfeld, eds. 1981. Vascular plant species of concern in Idaho. Forest, Wildlife and Range Experiment Station, Moscow, ID. 161 pp.