Poa fendleriana

(Steud.) Vasey

Muttongrass

G5Secure Found in 25 roadless areas NatureServe Explorer →
G5SecureGlobal Rank
UnknownThreat Impact
Identity
Unique IDELEMENT_GLOBAL.2.148393
Element CodePMPOA4Z0V0
Record TypeSPECIES
ClassificationSpecies
Classification StatusStandard
Name CategoryVascular Plant
Endemicoccurs (regularly, as a native taxon) in multiple nations
KingdomPlantae
PhylumAnthophyta
ClassMonocotyledoneae
OrderCyperales
FamilyPoaceae
GenusPoa
Other Common Names
muttongrass (EN) Pâturin de Fendler (FR)
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
This species hybridizes other Poa including Poa cusickii ssp. pallida, which results in the stable, apomictic taxon Poa x nematophylla (Howard 1997, FNA vol. 24, 2007).
Conservation Status
Rank Method Rank calculation - Biotics v2
Review Date2024-12-30
Change Date1997-09-17
Edition Date2024-12-30
Edition AuthorsEberly (2024)
Threat ImpactUnknown
Range Extent>2,500,000 square km (greater than 1,000,000 square miles)
Number of Occurrences> 300
Rank Reasons
Poa fendleriana is a wide ranging C3 perennial grass occurring across much of the western United States, southwestern Canada, and Mexico. With a large range extent, more than 1,000 occurrences, abundant habitat, broad habitat preferences, and no intrinsic vulnerabilities, this species is considered secure. See P.f. ssp. albescens, P.f. ssp. fendleriana, and P.f. ssp. longiligula for additional information.
Range Extent Comments
Poa fendleriana occurs in western Canada, the western United States, and Mexico from British Columbia to Manitoba and south to Mexico with occurrences in the Great Basin and Colorado Plateaus, Sierra Nevadas, and the Rocky Mountains (Soreng and van Devender 1989, FNA 2007, Soreng and Peterson 2012). Range extent was estimated using herbarium specimens and photo-based observations documented between 1983 and 2024 (GBIF 2024, iNaturalist 2024, SEINet 2024). Three subspecies are recognized: P.f. ssp. albescens is largely found in Sierra Occidental of Sonora and Chihuahua, Mexico and southeastern Arizona and southwestern New Mexico at the northern edge of the species range; P.f. ssp. fendleriana of Sonora, Mexico and north to Utah, Colorado, and the Dakotas; and P.f. ssp. longiligula occurs from from Baja California (Mexico) north to southwestern Canada with a tendency to have a more westward distribution than the other subspecies (Howard 1997, FNA 2007). Intermediate plants are found where ranges transition and overlap. See each of these taxa for additional conservation information.
Occurrences Comments
By applying a 1 km separation distance to herbarium records and photo-based observations documented between 1983 and 2024, it is estimated that there are over 1,400 occurrences rangewide (GBIF 2024, iNaturalist 2024, SEINet 2024).
Threat Impact Comments
Although threats are not widely documented, this species is desirable forage for grazing livestock. In some areas, excessive grazing will eliminate plants, but it is thought to tolerate moderately heavy grazing. Rotational grazing is implemented to maintain the forage species for livestock. The species response to fire is variable, from beneficial to harmful depending on timing, frequency, and intensity and whether the habitat is fire-maintained (Howard 1997, Simic et al. 2023). It can sprout from burned plants and reestablish post-fire from seeds (Howard 1997). This species is competitive with some exotic species; adult plants of Poa fendleriana are shown to suppress the invasion of Bromus tectorum (Porensky et al. 2021).
Ecology & Habitat

Habitat

This species grows on rocky to rich slopes in sagebrush-scrub, interior chaparral, and southern (rarely northern) high plains grasslands to riparian zones to forests and woodlands (scrub-oak, pinyon-juniper, mountain brush, ponderosa pine, fir-spruce communities; Arizona Cypress (Cupressus arizonica) woodland), and from desert hills to low alpine habitats and talus slopes, with elevations ranging from 910 to 4,000 meters (Howard 1997, FNA 2007).

Reproduction

This species is dioecious and has regions of sexual reproduction where seed set is limited and where staminate plants are common. By contrast, regions with only apomictic, pistillate plants are highly fecund (FNA 2007).
Terrestrial Habitats
Forest/WoodlandWoodland - HardwoodWoodland - ConiferShrubland/chaparralGrassland/herbaceousDesertAlpine
Other Nations (2)
CanadaN5
ProvinceRankNative
AlbertaS2Yes
ManitobaS2Yes
British ColumbiaS5Yes
SaskatchewanS3Yes
United StatesN5
ProvinceRankNative
South DakotaSNRYes
IdahoSNRYes
OregonSNRYes
CaliforniaSNRYes
OklahomaSNRYes
MontanaS4Yes
UtahSNRYes
WyomingS4Yes
North DakotaSNRYes
NevadaS4Yes
New MexicoSNRYes
WashingtonSNRYes
TexasSNRYes
NebraskaS3Yes
ArizonaSNRYes
ColoradoS4Yes
Threat Assessments
ThreatScopeSeverityTiming
2 - Agriculture & aquacultureRestricted (11-30%)Negligible or <1% pop. declineHigh (continuing)
2.3 - Livestock farming & ranchingRestricted (11-30%)Negligible or <1% pop. declineHigh (continuing)
2.3.1 - Nomadic grazingRestricted (11-30%)Negligible or <1% pop. declineHigh (continuing)
7 - Natural system modificationsLarge - restrictedUnknownHigh (continuing)
7.1 - Fire & fire suppressionLarge - restrictedUnknownHigh (continuing)
7.1.1 - Increase in fire frequency/intensityLarge - restrictedUnknownHigh (continuing)

Plant Characteristics
DurationPERENNIAL
Economic Value (Genus)No
Roadless Areas (25)
Arizona (3)
AreaForestAcres
Happy ValleyCoronado National Forest7,972
Santa RitaCoronado National Forest6,078
Upper Rincon RoadlessCoronado National Forest2,991
Montana (2)
AreaForestAcres
Electric PeakBeaverhead-Deerlodge National Forest17,997
West Big HoleBeaverhead-Deerlodge National Forest133,563
Nevada (4)
AreaForestAcres
Fourmile HillHumboldt-Toiyabe National Forest15,718
The Cove 1Humboldt-Toiyabe National Forest2,847
Wellington HillsHumboldt-Toiyabe National Forest21,009
WilhoitesHumboldt-Toiyabe National Forest11,297
New Mexico (10)
AreaForestAcres
Black CanyonSanta Fe National Forest1,922
Chama WS RiverSanta Fe National Forest4,168
Chama WildernessSanta Fe National Forest1,295
Gila BoxGila National Forest23,759
Juan de Gabaldon GrantSanta Fe National Forest8,023
Little TesuqueSanta Fe National Forest815
Nichols ReservoirSanta Fe National Forest1,518
RendijaSanta Fe National Forest2,176
Sawyers PeakGila National Forest59,743
Thompson PeakSanta Fe National Forest33,001
Utah (6)
AreaForestAcres
Bullion - DelanoFishlake National Forest14,917
Right Hand Fork LoganWasatch-Cache National Forest15,023
Shakespeare PointDixie National Forest753
Stansbury MountainsWasatch-Cache National Forest39,696
Table Cliffs - Henderson CanyonDixie National Forest19,581
Tushar MountainFishlake National Forest39,992
References (10)
  1. Flora of North America Editorial Committee (FNA). 2007a. Flora of North America north of Mexico. Vol. 24. Magnoliophyta: Commelinidae (in part): Poaceae, part 1. Oxford Univ. Press, New York. xxviii + 911 pp.
  2. Global Biodiversity Information Facility (GBIF). 2024. Global Biodiversity Information Facility (GBIF) data portal. Online. Available: https://www.gbif.org/ (accessed 2024).
  3. Howard, J.L. 1997. <i>Poa fendleriana</i>. In: Fire Effects Information System. U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). Online. Available: https://www.fs.usda.gov /database/feis/plants/graminoid/poafen/all.html (accessed 30 Dec 2024).
  4. iNaturalist. 2024. Online. Available: https://www.inaturalist.org (accessed 2024).
  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. Porensky, L.M., O. Baughman, M.A. Williamson, B.L. Perryman, M.D. Madsen, and E.A. Leger. 2021. Using native grass seeding and targeted spring grazing to reduce low-level <i>Bromus tectorum</i> invasion on the Colorado Plateau. Biological Invasions 23:705–722. https://doi.org/10.1007/s10530-020-02397-0
  7. Simic, P.Z., J.D. Coop, E.Q. Margolis, J.R. Young, and M.K. Lopez. 2023. Historical Fire Regimes and Contemporary Fire Effects Within Sagebrush Habitats of Gunnison Sage-Grouse. Ecosphere 14(6):e4587. https://doi.org/10.1002/ecs2.4587
  8. Soreng, R. J., and Peterson, P. M. 2012. Revision of <i>Poa</i> L. (Poaceae, Pooideae, Poeae, Poinae) in Mexico: new records, re-evaluation of <i>P. ruprechtii</i>, and two new species, <i>P. palmeri</i> and <i>P. wendtii</i>. <i>PhytoKeys </i>5:1–104.
  9. Soreng, R.J. and T.R. van Devender. 1989. Late quaternary fossils of <i>Poa fendleriana</i> (muttongrass): Holocene expansions of apomicts. Southwestern Naturalist 34(1):35-45.
  10. Southwest Environmental Information Network (SEINet). 2024. Collections Databases. Online. Available: https://swbiodiversity.org/seinet/collections/index.php (accessed 2024).