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CEGL002354 Ephedra viridis / (Achnatherum hymenoides, Hesperostipa comata) Shrubland

Type Concept Sentence: No Data Available


Common (Translated Scientific) Name: Mormon-tea / (Indian Ricegrass, Needle-and-Thread) Shrubland

Colloquial Name: No Data Available

Hierarchy Level:  Association

Type Concept: This shrubland is known from southeastern Utah. The vegetation is characterized by an open canopy of clonal Ephedra viridis shrubs with between 5 and 20% cover with a well-developed grassy understory dominated by either Achnatherum hymenoides or Hesperostipa comata. The herbaceous layer totals up to 35% cover. Associated shrubs include scattered Coleogyne ramosissima, Atriplex canescens, Eriogonum leptocladon, and the succulent Opuntia polyacantha. Other grasses include Aristida purpurea, Muhlenbergia pungens, Sporobolus cryptandrus, and Bouteloua gracilis. If Pleuraphis jamesii is present, it is with much less cover than either Hesperostipa comata or Achnatherum hymenoides. Forbs include many species typical of sandy communities, including Abronia fragrans, Chaenactis stevioides, Cymopterus newberryi, Oenothera pallida, Machaeranthera canescens, Plantago patagonica, and Sphaeralcea parvifolia. Cryptogams are often present and provide up to 25% cover. Stands occur on sand dunes and sandsheets deposited on plateaus, benches and valley floors. Sites occupy gentle to moderately steep slopes (1-45%) between 1114 and 2018 m elevation. Soils are rapidly drained loamy sands and sandy loams derived from eolian sands or alluvial deposits.

Diagnostic Characteristics: No Data Available

Rationale for Nominal Species or Physiognomic Features: No Data Available

Classification Comments: This association is largely known and described from National Park Service inventory efforts in the Colorado Plateau.

Similar NVC Types: No Data Available
note: No Data Available

Physiognomy and Structure: No Data Available

Floristics: Stands of this association usually occur as patches of one to several hectares within a matrix of other sandy communities dominated by Coleogyne ramosissima and Artemisia filifolia, although occasionally it will be the matrix community. The appearance is that of a grassland containing large, low-growing clonal clumps of Ephedra viridis. Total vegetation cover ranges from 5 to 55% but generally is between 15 and 35%. The vegetation is characterized by an open canopy of Ephedra viridis shrubs with between 5 and 20% cover with a well-developed grassy understory dominated by either Achnatherum hymenoides or Hesperostipa comata. The herbaceous layer totals up to 35% cover. Associated shrubs include scattered Acamptopappus sphaerocephalus, Artemisia filifolia, Atriplex canescens, Atriplex confertifolia, Coleogyne ramosissima, Ephedra torreyana, Eriogonum leptocladon, Gutierrezia microcephala, Gutierrezia sarothrae, Opuntia polyacantha var. erinacea (= Opuntia erinacea), Opuntia polyacantha var. polyacantha, Psorothamnus fremontii, Sclerocactus whipplei, and Yucca angustissima. Other grasses include Aristida purpurea, Bouteloua gracilis, Muhlenbergia pungens, Pleuraphis jamesii, Schismus barbatus, Sporobolus airoides, Sporobolus contractus, Sporobolus cryptandrus, and Vulpia octoflora (= Festuca octoflora). If Pleuraphis jamesii is present, it is with much less cover than either Hesperostipa comata or Achnatherum hymenoides. Forbs include many species typical of sandy communities, including Abronia fragrans, Ambrosia acanthicarpa, Artemisia campestris, Chaenactis stevioides, Cryptantha sp., Cymopterus newberryi, Descurainia pinnata, Eriogonum deflexum, Helianthus petiolaris, Hymenopappus filifolius, Lappula occidentalis, Machaeranthera canescens, Mentzelia multiflora, Oenothera pallida, Packera multilobata (= Senecio multilobatus), Penstemon ambiguus, Plantago patagonica, Psoralidium junceum, and Sphaeralcea parvifolia. The exotic annual tumbleweed Salsola tragus and the exotic annual grass Bromus tectorum are common in some stands. Biological soil crusts are often present and provide up to 25% cover.

Dynamics:  This association occupies deep sand deposits that have formed as dune fields on sandsheets. Although these stands are stabilized, wind erosion can pedestal plants and leave deflation basins between. Historically, these habitats were heavily grazed which, along with drought, likely activated the erosion process. Ephedra viridis is known to sprout vigorously from the roots or woody rootcrowns or establish by seed following fire (Anderson 2001b). These fire adaptations may favor it over more fire-sensitive species such as Coleogyne ramosissima.

Environmental Description:  This short-shrub association occurs on sand dunes and sandsheets deposited on plateaus, benches and valley floors in southeastern Utah. Sites occupy gentle to moderately steep slopes (1-45%) between 1114 and 2018 m elevation and oriented to a variety of aspects, with a slight tendency toward northern and eastern aspects. The unvegetated surface has up to 96% sand or bare soil, with the balance covered by litter or dark cyanobacteria. Cover of cryptogamic soil communities is typically sparse (<10%) but ranges from none to 25%. Cover of litter is sparse to low. Soils are rapidly drained loamy sands and sandy loams derived from sandstones and shale that have eroded to eolian sands or alluvial deposits.

Geographic Range: This association occurs in the Colorado Plateau in southeastern Utah and likely occurs in adjacent states.

Nations: US

States/Provinces:  UT




Confidence Level: Moderate

Confidence Level Comments: No Data Available

Grank: GNR

Greasons: No Data Available


Concept Lineage: No Data Available

Predecessors: No Data Available

Obsolete Names: No Data Available

Obsolete Parents: No Data Available

Synonomy: = Ephedra viridis / (Achnatherum hymenoides, Hesperostipa comata) Shrubland (Clark et al. 2009)

Concept Author(s): Clark et al. (2009)

Author of Description: J. Coles, K.A. Schulz and G. Kittel

Acknowledgements: No Data Available

Version Date: 04-05-16

  • Anderson, M. D. 2001b. Ephedra viridis. In: Fire Effects Information System [Online]. USDA Forest Service, Rocky Mountain Research Station, Fire Sciences Laboratory (Producer). [http://www.fs.fed.us/database/feis/] (accessed 15 October 2007 and 19 June 2011).
  • Clark, D., M. Dela Cruz, T. Clark, J. Coles, S. Topp, A. Evenden, A. Wight, G. Wakefield, and J. Von Loh. 2009. Vegetation classification and mapping project report, Capitol Reef National Park. Natural Resource Report NPS/NCPN/NRTR--2009/187. National Park Service, Fort Collins, CO. 882 pp.
  • Coles, J., A. Tendick, G. Manis, A. Wight, G. Wakefield, J. Von Loh, and A. Evenden. 2009a. Vegetation classification and mapping project report, Arches National Park. Natural Resource Technical Report NPS/NCPN/NRTR--2009/253. National Park Service, Fort Collins, CO. 544 pp.
  • Romme, W. H., K. D. Heil, J. M. Porter, and R. Fleming. 1993. Plant communities of Capitol Reef National Park, Utah. USDI National Park Service, Technical Report NPS/NAUCARE/NRTER-93/02. Cooperative Park Studies Unit, Northern Arizona University. 37 pp.
  • Tendick, A., J. Coles, K. Decker, M. Hall, J. Von Loh, T. Belote, A. Wight, G. Wakefield, and A. Evenden. 2012. Vegetation classification and mapping project report, Canyonlands National Park. Natural Resource Technical Report NPS/NCPN/NRTR--2012/577. National Park Service, Fort Collins, CO.
  • Tendick, A., J. Spence, M. Reid, K. Shulz, G. Kittel, K. Green, A. Wight, and G. Wakefield. 2017. Vegetation classification and mapping project report, Glen Canyon National Recreation Area and Rainbow Bridge National Monument. Natural Resource Report NPS/NCPN/NRR—2017/1500. National Park Service, Fort Collins, CO. 1464 pp.
  • Western Ecology Working Group of NatureServe. No date. International Ecological Classification Standard: International Vegetation Classification. Terrestrial Vegetation. NatureServe, Boulder, CO.