Print Report
CEGL001017 Artemisia tridentata ssp. tridentata / Pascopyrum smithii - (Elymus lanceolatus) Shrubland
Type Concept Sentence: No Data Available
Common (Translated Scientific) Name: Basin Big Sagebrush / Western Wheatgrass - (Thick-spike Wheatgrass) Shrubland
Colloquial Name: No Data Available
Hierarchy Level: Association
Type Concept: This widespread sagebrush shrubland occurs on valley bottoms, stream terraces and other relatively mesic sites west of the Great Plains throughout much of the intermountain western U.S. Stands occur over an elevational range of 1800-2410 m (5900-7900 feet). Most stands grow on alluvial terraces in stream alluvium, although a few occur on upland swales. Soils generally are loamy or sandy. Water tables may be within 2 m of the soil surface. The stream channel often is dry and may be incised. Soils are moderately well-drained sandy loam to sandy clay loam derived from alluvium. This association is characterized by a sparse to moderately dense short-shrub layer (up to about 40% canopy cover and to 1.5 m tall) that is dominated by Artemisia tridentata ssp. tridentata, with an herbaceous layer that is usually dominated by Pascopyrum smithii or Elymus lanceolatus. Other shrubs may be present in small amounts, especially Artemisia tridentata ssp. wyomingensis, Chrysothamnus viscidiflorus, Ericameria nauseosa, Ericameria parryi, Krascheninnikovia lanata, or Quercus gambelii. The sparse to dense herbaceous layer is dominated by graminoids and is poor in species richness relative to other sagebrush types. Other species that may be present in substantial amounts are Achnatherum hymenoides, Achnatherum pinetorum, Bromus inermis, Elymus elymoides, Leymus cinereus, Muhlenbergia richardsonis, Poa fendleriana, Poa secunda, and introduced species Bromus inermis and Poa pratensis. Forbs contribute much less cover than do grasses. Species that often occur are Achillea millefolium, Astragalus spp., Erigeron compositus, Packera cana, Penstemon spp., Symphyotrichum ascendens, and introduced species Taraxacum officinale and Melilotus officinalis.
Diagnostic Characteristics: No Data Available
Rationale for Nominal Species or Physiognomic Features: No Data Available
Classification Comments: No Data Available
Similar NVC Types: No Data Available
note: No Data Available
Physiognomy and Structure: No Data Available
Floristics: This association is characterized by a sparse to moderately dense short-shrub layer (up to about 40% canopy cover and to 1.5 m tall) that is dominated by Artemisia tridentata ssp. tridentata, with an herbaceous layer that is usually dominated by Pascopyrum smithii or Elymus lanceolatus. Other shrubs may be present in small amounts, especially Artemisia tridentata ssp. wyomingensis, Chrysothamnus viscidiflorus, Ericameria nauseosa (= Chrysothamnus nauseosus), Ericameria parryi, Krascheninnikovia lanata, or Quercus gambelii. The sparse to dense herbaceous layer is dominated by graminoids and is poor in species richness relative to other sagebrush types. Other species that may be present in substantial amounts are Achnatherum hymenoides, Achnatherum pinetorum, Bromus inermis, Elymus elymoides, and Poa fendleriana in Colorado (Tiedemann et al. 1987), Poa secunda (= Poa nevadensis) and Muhlenbergia richardsonis in Nevada (Blackburn et al. 1971), and Leymus cinereus and Poa pratensis in Montana (Cooper et al. 1995). Forbs contribute much less cover than do grasses. Species that often occur are Symphyotrichum ascendens (= Aster ascendens) and Collinsia parviflora in Nevada (Blackburn et al. 1971), Achillea millefolium, Astragalus convallarius, Astragalus drummondii, Astragalus tenellus, Penstemon strictus, and Penstemon caespitosus in north-central Colorado (Tiedemann et al. 1987), Achillea millefolium, Erigeron compositus, Packera cana (= Senecio canus), and Taraxacum officinale in southwestern Montana (Cooper et al. 1995), and Cordylanthus ramosus in southwestern Wyoming (Jones and Fertig 1996). Mosses and lichens may be important ground cover.
Dynamics: Artemisia tridentata shrubs are killed by burns and do not resprout (Wright et al. 1979). Artemisia tridentata will re-establish relatively quickly (about 10-20 years) if a seed source is nearby (Bunting 1987). If fire-return intervals are more frequent than 10 years, then Artemisia tridentata has difficulty recovering (Bunting 1987, Everett 1987).
Environmental Description: This widespread sagebrush shrubland occurs on valley bottoms, stream terraces and other relatively mesic sites west of the Great Plains. Stands occur over an elevational range of 1800-2410 m (5900-7900 feet). Most stands grow on alluvial terraces in stream alluvium, although a few occur on upland swales. Soils generally are loamy or sandy. Water tables may be within 2 m of the soil surface. The stream channel often is dry and may be incised. Soils are moderately well-drained sandy loam to sandy clay loam derived from alluvium.
Geographic Range: This association occurs across the interior western U.S. from southwestern Montana, southwestern Wyoming, and north-central Colorado to southwestern Utah and northeastern Nevada. It may also occur in Washington, Oregon, and Idaho given the broad geographic ranges of Artemisia tridentata ssp. tridentata and Pascopyrum smithii.
Nations: US
States/Provinces: CO, ID?, MT, NV, OR?, UT, WA?, WY
Plot Analysis Summary:
http://vegbank.org/natureserve/ELEMENT_GLOBAL.2.684272
Confidence Level: Moderate
Confidence Level Comments: No Data Available
Grank: G3?
Greasons: No Data Available
Type | Name | Database Code | Classification Code |
---|---|---|---|
Class | 3 Desert & Semi-Desert Class | C03 | 3 |
Subclass | 3.B Cool Semi-Desert Scrub & Grassland Subclass | S11 | 3.B |
Formation | 3.B.1 Cool Semi-Desert Scrub & Grassland Formation | F033 | 3.B.1 |
Division | 3.B.1.Ne Western North American Cool Semi-Desert Scrub & Grassland Division | D040 | 3.B.1.Ne |
Macrogroup | 3.B.1.Ne.3 Big Sagebrush - Threetip Sagebrush - Antelope Bitterbrush Steppe & Shrubland Macrogroup | M169 | 3.B.1.Ne.3 |
Group | 3.B.1.Ne.3.b Basin Big Sagebrush - Threetip Sagebrush - Antelope Bitterbrush Big Sagebrush Steppe & Shrubland Group | G302 | 3.B.1.Ne.3.b |
Alliance | A3183 Basin Big Sagebrush - Foothill Big Sagebrush Mesic Steppe & Shrubland Alliance | A3183 | 3.B.1.Ne.3.b |
Association | CEGL001017 Basin Big Sagebrush / Western Wheatgrass - (Thick-spike Wheatgrass) Shrubland | CEGL001017 | 3.B.1.Ne.3.b |
Concept Lineage: No Data Available
Predecessors: No Data Available
Obsolete Names: No Data Available
Obsolete Parents: No Data Available
Synonomy: ? Artemisia tridentata / Agropyron smithii Community Type (Blackburn et al. 1971)
? Artemisia tridentata / Elytrigia smithii Plant Association (Johnston 1987) [Johnston (1987) does not specify the subspecies of big sagebrush.]
> Artemisia tridentata ssp. tridentata / Agropyron smithii Community Type (Cooper et al. 1995)
< Artemisia tridentata ssp. tridentata / Agropyron smithii habitat type (Tiedemann et al. 1987)
< Artemisia tridentata ssp. tridentata / Agropyron smithii habitat type (Strong 1980) [Strong''s information on the composition of the vegetation on his habitat type was taken from work that led to Tiedemann et al.''s (1987) habitat type description.]
= Artemisia tridentata tridentata / Agropyron smithii Habitat Type (Francis 1983)
< Poa nevadensis / Carex sp. Habitat Type (Blackburn et al. 1971) [supports stands of their Artemisia tridentata / Agropyron smithii Community Type, which apparently belongs to this association (they did not specify the subspecies of Artemisia tridentata, but the habitat is similar to that described in reports elsewhere).]
? Artemisia tridentata / Elytrigia smithii Plant Association (Johnston 1987) [Johnston (1987) does not specify the subspecies of big sagebrush.]
> Artemisia tridentata ssp. tridentata / Agropyron smithii Community Type (Cooper et al. 1995)
< Artemisia tridentata ssp. tridentata / Agropyron smithii habitat type (Tiedemann et al. 1987)
< Artemisia tridentata ssp. tridentata / Agropyron smithii habitat type (Strong 1980) [Strong''s information on the composition of the vegetation on his habitat type was taken from work that led to Tiedemann et al.''s (1987) habitat type description.]
= Artemisia tridentata tridentata / Agropyron smithii Habitat Type (Francis 1983)
< Poa nevadensis / Carex sp. Habitat Type (Blackburn et al. 1971) [supports stands of their Artemisia tridentata / Agropyron smithii Community Type, which apparently belongs to this association (they did not specify the subspecies of Artemisia tridentata, but the habitat is similar to that described in reports elsewhere).]
- Beetle, A. A., and K. L. Johnson. 1982. Sagebrush in Wyoming. Wyoming Agricultural Experiment Station Bulletin 779. University of Wyoming, Laramie.
- Blackburn, W. H., P. T. Tueller, and R. E. Eckert, Jr. 1971. Vegetation and soils of the Rock Springs watershed. Nevada Agricultural Experiment Station Bulletin R-83. Reno. 116 pp.
- Bourgeron, P. S., and L. D. Engelking, editors. 1994. A preliminary vegetation classification of the western United States. Unpublished report. The Nature Conservancy, Western Heritage Task Force, Boulder, CO. 175 pp. plus appendix.
- Bunting, S. C. 1987. Use of prescribed burning in juniper and pinyon-juniper woodlands. Pages 141-144 in: R. L. Everett, compiler. Proceedings--pinyon-juniper conference; 1986 January 13-16; Reno, NV. General Technical Report INT-215. USDA Forest Service, Intermountain Research Station, Ogden, UT.
- CNHP Ecology Team [Colorado Natural Heritage Program Ecology Team]. 2001. A classification of the native vegetation of Colorado. Colorado Natural Heritage Program, Colorado State University, Fort Collins.
- CNHP [Colorado Natural Heritage Program]. 2006-2017. Tracked natural plant communities. Colorado Natural Heritage Program, Colorado State University, Fort Collins. [https://cnhp.colostate.edu/ourdata/trackinglist/plant_communities/]
- Cogan, D., M. Reid, K. Schulz, and M. Pucherelli. 2004. Zion National Park, Utah 1999-2003. Vegetation Mapping Project. Technical Memorandum 8260-03-01. Remote Sensing and GIS Group Technical Service Center, Bureau of Reclamation, Denver, CO. Appendix F: Vegetation Association Descriptions for Zion.
- Coles, J., A. Tendick, J. Von Loh, G. Bradshaw, G. Manis, A. Wight, G. Wakefield, and A. Evenden. 2010. Vegetation classification and mapping project report, Black Canyon of the Gunnison National Park. Natural Resource Technical Report NPS/NCPN/NRTR--2010/361. National Park Service, Fort Collins, CO.
- Cooper, S. V., P. Lesica, R. L. DeVelice, and T. McGarvey. 1995. Classification of southwestern Montana plant communities with emphasis on those of Dillon Resource Area, Bureau of Land Management. Montana Natural Heritage Program, Helena, MT. 154 pp.
- Everett, R. L. 1987. Plant response to fire in the pinyon-juniper zone. Pages 152-157 in R. L. Everett, compiler. Proceedings pinyon-juniper conference: 1986 January 13-16, Reno, NV. General Technical Report INT-215. USDA Forest Service, Intermountain Research Station, Ogden, UT.
- Francis, R. E. 1983. Sagebrush-steppe habitat types in northern Colorado: A first approximation. Pages 67-71 in: Proceedings of the Workshop on Southwestern habitat types. USDA Forest Service, Southwestern Region, Albuquerque, NM.
- Johnston, B. C. 1987. Plant associations of Region Two: Potential plant communities of Wyoming, South Dakota, Nebraska, Colorado, and Kansas. R2-ECOL-87-2. USDA Forest Service, Rocky Mountain Region. Lakewood, CO. 429 pp.
- Jones, G. P., and W. Fertig. 1996. Plant associations and plant species of special concern in the Jack Morrow Hills ecosystem. Unpublished report prepared for the Bureau of Land Management, Rock Springs District by the Wyoming Natural Diversity Database. 2 volumes.
- Keammerer, W. R. 1977. Final report: Vegetation baseline studies, oil shale tract C-b. Unpublished report. Stoecker-Keammerer and Associates, Ecological Consultants, Boulder, CO. 183 pp.
- MTNHP [Montana Natural Heritage Program]. 2002b. List of ecological communities for Montana. Montana Natural Heritage Program, Montana State Library, Helena, MT.
- Peterson, E. B. 2008. International Vegetation Classification alliances and associations occurring in Nevada with proposed additions. Nevada Natural Heritage Program, Carson City, NV. 348 pp.
- Strong, L. L. 1980. Estimating phytomass production of habitat types on sagebrush steppe. Unpublished thesis, Colorado State University, Fort Collins. 133 pp.
- Tendick, A., J. Coles, P. Williams, G. Bradshaw, G. Manis, A. Wight, G. Wakefield, and A. Evenden. 2010. Vegetation classification and mapping project report, Curecanti National Recreation Area. Natural Resource Technical Report NPS/NCPN/NRTR--2010/408. National Park Service, Fort Collins, CO. 797 pp.
- Thomas, K. A., M. L. McTeague, L. Ogden, M. L. Floyd, K. Schulz, B. Friesen, T. Fancher, R. Waltermire, and A. Cully. 2009b. Vegetation classification and distribution mapping report: Mesa Verde National Park. Natural Resource Report NPS/SCPN/NRR--2009/112. National Park Service, Fort Collins, CO. 352 pp.
- Tiedemann, J. A., R. E. Francis, C. Terwilliger, Jr., and L. H. Carpenter. 1987. Shrub-steppe habitat types of Middle Park, Colorado. Research Paper RM-273. USDA Forest Service, Rocky Mountain Forest and Range Experiment Station, Fort Collins, CO. 20 pp.
- WNDD [Wyoming Natural Diversity Database]. No date. Unpublished data on file. Wyoming Natural Diversity Database, University of Wyoming, Laramie, WY.
- Western Ecology Working Group of NatureServe. No date. International Ecological Classification Standard: International Vegetation Classification. Terrestrial Vegetation. NatureServe, Boulder, CO.
- Wright, H. A., L. F. Neuenschwander, and C. M. Britton. 1979. The role and use of fire in sagebrush-grass and pinyon-juniper plant communities: A state of the art review. General Technical Report INT-58. USDA Forest Service, Intermountain Forest and Range Experiment Station, Ogden, UT.