Print Report
A3179 Purshia tridentata - Artemisia tridentata Mesic Steppe & Shrubland Alliance
Type Concept Sentence: This mesic alliance occurs throughout the Intermountain West and is characterized by an open to moderately dense short-shrub layer dominated or codominated by Purshia tridentata with Artemisia tridentata and sometimes Prunus virginiana present to codominant. The understory is sparse to dense and typically dominated by perennial bunchgrasses such as Achnatherum hymenoides, Achnatherum nelsonii, Achnatherum occidentale, Festuca campestris, Festuca idahoensis, Hesperostipa comata, Leymus cinereus, Poa secunda, and Pseudoroegneria spicata.
Common (Translated Scientific) Name: Antelope Bitterbrush - Big Sagebrush Mesic Steppe & Shrubland Alliance
Colloquial Name: Antelope Bitterbrush - Big Sagebrush Mesic Steppe & Shrubland
Hierarchy Level: Alliance
Type Concept: This mesic shrubland and steppe alliance occurs throughout the Intermountain West and occurs over a broad range of landforms and microhabitats. Stands are characterized by an open to moderately dense short-shrub layer dominated or codominated by Purshia tridentata with Artemisia tridentata and sometimes Prunus virginiana present to codominant. Other important shrubs include Ericameria nauseosa, Eriogonum heracleoides, Ribes cereum, and Symphoricarpos oreophilus. The understory is sparse to dense and typically dominated by perennial bunchgrasses such as Achnatherum hymenoides, Achnatherum nelsonii, Achnatherum occidentale, Festuca campestris, Festuca idahoensis, Hesperostipa comata, Leymus cinereus, Poa secunda, and Pseudoroegneria spicata. Some stands may have a well-developed forb component composed of Arabis holboellii, Achillea millefolium, Balsamorhiza sagittata, Brodiaea spp., Eriogonum ovalifolium, Eriogonum umbellatum, Lithospermum ruderale, and Pteryxia terebinthina. Mosses and lichens are important in some stands. Scattered trees may form an emergent layer of individual trees. Stands occur on flats to moderate slopes in foothills, on slopes of lakebeds with ash or pumice soils, and on drier sites within lower forest zones as shrub-steppe inclusions in forest. In Idaho, the alliance is reported from stabilized dunes. In general, it is an upland type associated with coarse, well-drained soils without high salinity or pH. Adjacent vegetation is typically Artemisia steppe, Pseudoroegneria - Poa - Festuca grasslands, or Pinus flexilis woodlands.
Diagnostic Characteristics: Stands in this mesic shrubland and steppe alliance are dominated or codominated by Purshia tridentata with Artemisia tridentata and sometimes Prunus virginiana present to codominant. Characteristic herbaceous species are Achnatherum hymenoides, Achnatherum nelsonii, Achnatherum occidentale, Carex pensylvanica, Eriogonum umbellatum, Festuca campestris, Festuca idahoensis, Hesperostipa comata, Leymus cinereus, Poa secunda, and Pseudoroegneria spicata.
Rationale for Nominal Species or Physiognomic Features: No Data Available
Classification Comments: This mesic shrubland and steppe alliance occurs as large patch/matrix stands in relatively mesic northern latitudes. However, in semi-arid landscapes in more southern latitudes, it frequently occurs in smaller patch stands restricted to relatively mesic sites, such as swales and basins, that receive additional moisture from surrounding slopes and at higher elevations.
Similar NVC Types: No Data Available
note: No Data Available
Physiognomy and Structure: This alliance has a moderately dense to open (20-60% cover) microphyllous evergreen (or late cold-deciduous) shrublands with the dominant shrubs varying from 0.5-3 m in height. Maximum shrub height generally decreases with latitude and altitude, reaching a minimum in subalpine stands. A second tier of microphyllous evergreen or cold-deciduous shrubs may be present. Cespitose graminoids are typical herbaceous associates and may strongly dominate the ground layer. Some regional variants may have a substantial forb component as well. Lichens and mosses may cover the ground surface in good condition stands.
Floristics: This mesic shrubland and steppe alliance is characterized by an open to moderately dense short-shrub layer dominated or codominated by Purshia tridentata with Artemisia tridentata and sometimes Prunus virginiana present to codominant. Other important or occasional shrubs include Artemisia frigida, Ceanothus velutinus, Chrysothamnus viscidiflorus, Ericameria nauseosa (= Chrysothamnus nauseosus), Eriogonum heracleoides, Ribes cereum, and Symphoricarpos oreophilus. Scattered trees may form an emergent layer of individual trees; species include Cercocarpus ledifolius, Juniperus occidentalis, Juniperus osteosperma, Juniperus scopulorum, Pinus ponderosa, Pinus jeffreyi, Pinus ponderosa var. washoensis (= Pinus washoensis), Quercus garryana, or Yucca brevifolia. The understory is sparse to dense and typically dominated by perennial bunchgrasses such as Achnatherum hymenoides, Achnatherum nelsonii, Achnatherum occidentale, Elymus lanceolatus, Festuca campestris, Festuca idahoensis, Hesperostipa comata, Koeleria macrantha, Leymus cinereus, , Poa secunda, and Pseudoroegneria spicata. Other graminoids include Carex geyeri, Carex pensylvanica, and Muhlenbergia montana. Some stands may have a well-developed forb component composed of Arabis holboellii, Achillea millefolium, Balsamorhiza sagittata, Brodiaea spp., Eriogonum ovalifolium, Eriogonum umbellatum, Lithospermum ruderale, and Pteryxia terebinthina (= Cymopterus terebinthinus). Mosses and lichens are important in some stands. Diagnostic of this alliance is the dominance of Purshia tridentata in a shrub layer that is greater than 25% on average.
Dynamics: Purshia tridentata displays considerable plasticity in growth across its range. The variation in height and form of different populations appears to be related to ecotypic variation (Mozingo 1987). Although mycorrhizae are considered important in establishment and growth of individual plants, Purshia tridentata is one of the first species to colonize barren volcanic substrates following eruption. The species is valuable as winter browse for native ungulates and livestock and is used extensively. Moderate livestock utilization (<60% of the year''s current growth) has been reported to stimulate twig growth the following spring (Mueggler and Stewart 1980). Sawyer and Keeler-Wolf (1995) report that stands of Purshia tridentata can reach 125 years of age on deep, well-drained sites, but more commonly become decadent at 30 years, and die at 40-50 years of age. Stands appear to result from either a disturbance event (such as fire), or from rare years when many seedlings survive. This results in even-aged stands (Sawyer and Keeler-Wolf 1995).
Environmental Description: This mesic shrubland and steppe alliance occurs throughout the Intermountain West over a broad range of landforms and microhabitats at elevations from 500-3000 m. Stands are often found on the margins of Pinus ponderosa woodlands or forests, forming the transition into sagebrush vegetation. Most of the region is arid to semi-arid with annual precipitation ranging from 15-75 cm. The entire range is under a continental temperature regime of cold winters, cool to warm summers and large diurnal variation. In the western portions of the alliance''s range, summers are dry. Growing-season precipitation increases eastward and is the greatest in the Rocky Mountains. They also occur on flats to moderate slopes in foothills, on slopes of lakebeds with ash or pumice soils, and on drier sites within lower forest zones as shrub-steppe inclusions in forest. In Idaho, the alliance is reported from stabilized dunes (Chadwick and Dalke 1965). In Colorado, the alliance is found on exposed, steep (45-60% slope) mountain slopes with southerly aspects on the eastern slopes of the Front Range (Hess 1981). These sites are typically too xeric to support extensions of the surrounding coniferous forests. Parent materials are colluvial and residual metamorphic rocks which have developed into soils classified as Entisols. These soils are poorly developed and rocky, with loamy and sandy textures, and shallow A horizons over rocky C horizons. The soil surface is also moderately rocky. In general, it is an upland type associated with coarse, well-drained soils without high salinity or pH. Adjacent vegetation is typically Artemisia steppe, Pseudoroegneria - Poa - Festuca grasslands, or Pinus flexilis woodlands.
Geographic Range: This alliance is found in many western U.S. states and Canada, from California north and east into Oregon, Washington, Idaho, Colorado and British Columbia. The core of its range is the Columbia Basin and Columbia Plateau, Owyhee Uplands, Snake River Plain, and the Colorado Rockies. Purshia tridentata is one of the most widespread shrubs in the western United States.
Nations: CA,US
States/Provinces: BC, CA, ID, MT, NV, OR, UT, WA, WY
Plot Analysis Summary:
http://vegbank.org/natureserve/ELEMENT_GLOBAL.2.899304
Confidence Level: Moderate
Confidence Level Comments: No Data Available
Grank: GNR
Greasons: No Data Available
Concept Lineage: A.825, A.1517, A.1523. This alliance includes proto alliances Purshia tridentata Shrubland Alliance (A.825), Purshia tridentata Shrub Herbaceous Alliance (A.1523) and old alliances III.A.4.N.a. Purshia tridentata Shrubland Alliance (A.825), V.A.7.N.b. Purshia tridentata Shrub Tall Herbaceous Alliance (A.1517), V.A.7.N.e. Purshia tridentata Shrub Herbaceous Alliance (A.1523). and one association from old alliance III.A.4.N.a. Artemisia tridentata ssp. wyomingensis Shrubland Alliance (A.832).
Predecessors: No Data Available
Obsolete Names: No Data Available
Obsolete Parents: No Data Available
Synonomy: > Purshia tridentata (Bitter brush scrub) Alliance (Sawyer et al. 2009) [35.200.00]
>< Bitterbrush Series (Sawyer and Keeler-Wolf 1995)
>< Bitterbrush Series (Sawyer and Keeler-Wolf 1995)
- Buttery, R. F. 1955. Range conditions and trends resulting from winter concentrations of elk in Rocky Mountain National Park, Colorado. Unpublished thesis. Colorado Agricultural and Mechanical College, Fort Collins. 117 pp.
- Caicco, S. L., and C. A. Wellner. 1983e. Research Natural Area recommendation for St. Anthony Sand Dunes. Unpublished report prepared for USDI Bureau of Land Management, Idaho Falls District, Idaho by Idaho Natural Areas Coordinating Committee. 10 pp.
- Chadwick, H. W., and P. D. Dalke. 1965. Plant succession on dune sands in Fremont County, Idaho. Ecology 46:765-780.
- Chappell, C., R. Crawford, J. Kagan, and P. J. Doran. 1997. A vegetation, land use, and habitat classification system for the terrestrial and aquatic ecosystems of Oregon and Washington. Unpublished report prepared for Wildlife habitat and species associations within Oregon and Washington landscapes: Building a common understanding for management. Prepared by Washington and Oregon Natural Heritage Programs, Olympia, WA, and Portland, OR. 177 pp.
- Copeland, W. N. 1978. Botanical survey of Eight Dollar Mountain, May 6-9, 1978. Oregon Natural Heritage Data Base, Portland, OR.
- Daubenmire, R. 1975. Floristic plant geography of eastern Washington and northern Idaho. Journal of Biogeography 2:1-18.
- Daubenmire, R. F. 1970. Steppe vegetation of Washington. Washington State University Agricultural Experiment Station Technical Bulletin No. 62. 131 pp.
- Day, T. A. 1985. Plant association and soil factors in primary succession on cinder cones in Idaho. Unpublished thesis, University of Idaho, Moscow. 62 pp.
- Day, T. A., and R. G. Wright. 1985. The vegetation types of Craters of the Moon National Monument. Forestry, Wildlife, and Range Experiment Station Bulletin No. 38. University of Idaho, Moscow. 6 pp.
- Evens, J. M., K. Sikes, D. Hastings, and J. Ratchford. 2014. Vegetation alliance descriptions for Lake Mead National Recreation Area, Death Valley National Park and Mojave National Preserve. Unpublished report submitted to USDI National Park Service, Mojave Desert Network Inventory and Monitoring Program. California Native Plant Society, Sacramento, CA.
- Faber-Langendoen, D., J. Drake, M. Hall, G. Kittel, S. Menard, C. Nordman, M. Pyne, M. Reid, M. Russo, K. Schulz, L. Sneddon, K. Snow, and J. Teague. 2013-2019b. Screening alliances for induction into the U.S. National Vegetation Classification: Part 1 - Alliance concept review. NatureServe, Arlington, VA.
- Franklin, J. F., and C. T. Dyrness. 1973. Natural vegetation of Oregon and Washington. General Technical Report PNW-8. USDA Forest Service, Pacific Northwest Forest and Range Experiment Station, Portland, OR. 417 pp.
- Hall, F. C. 1973. Plant communities of the Blue Mountains in eastern Oregon and southeastern Washington. R6 Area Guide 3-1. USDA Forest Service, Pacific Northwest Region, Portland, OR. 62 pp.
- Hess, K. 1981. Phyto-edaphic study of habitat types of the Arapaho-Roosevelt National Forest, Colorado. Unpublished dissertation, Colorado State University, Fort Collins. 558 pp.
- Hess, K., and C. H. Wasser. 1982. Grassland, shrubland, and forest habitat types of the White River-Arapaho National Forest. Unpublished final report 53-82 FT-1-19. USDA Forest Service, Rocky Mountain Forest and Range Experiment Station, Fort Collins, CO. 335 pp.
- Hironaka, M., M. A. Fosberg, and A. H. Winward. 1983. Sagebrush-grass habitat types of southern Idaho. Forestry, Wildlife, and Range Experiment Station Bulletin No. 15, University of Idaho, Moscow. 44 pp.
- Johnson, C. G., Jr., and S. A. Simon. 1987. Plant associations of the Wallowa-Snake Province Wallowa-Whitman National Forest. Technical Paper R6-ECOL-TP-255A-86. USDA Forest Service, Pacific Northwest Region, Wallowa-Whitman National Forest. 399 pp. plus appendices.
- Johnson, C. G., and R. R. Clausnitzer. 1992. Plant associations of the Blue and Ochoco mountains. R6-ERW-TP-036-92. USDA Forest Service, Pacific Northwest Region, Wallowa-Whitman National Forest. 163 pp. plus appendices.
- 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.
- Lewis, M. E. 1975a. Plant communities of the Jarbidge Mountain Complex, Humboldt National Forest. Unpublished report compiled for USDA Forest Service, Region IV, Ogden, UT. 22 pp.
- Marr, J. W., D. M. Armstrong, H. Chronic, J. Chronic, R. W. Pennak, W. A. Weber, R. E. Marr, D. Steward, and J. C. Meyer. 1980. Natural landmarks of the southern Rocky Mountain region. Unpublished report prepared for USDI Heritage Conservation and Recreation Service, Denver, CO, by Thorne Ecological Institute, Boulder, CO. 736 pp.
- Moseley, R. K. 1987c. Idaho preserve design package: Formation Spring, Caribou County, Idaho. Unpublished report prepared by The Nature Conservancy, Idaho Field Office, Ketchum, ID. 9 pp.
- Mozingo, H. 1987. Shrubs of the Great Basin: A natural history. University of Nevada Press, Las Vegas. 342 pp.
- Mueggler, W. F., and W. L. Stewart. 1980. Grassland and shrubland habitat types of western Montana. General Technical Report INT-66. USDA Forest Service, Intermountain Forest and Range Experiment Station, Ogden, UT. 154 pp.
- Poulton, C. E. 1955. Ecology of the non-forested vegetation in Umatilla and Morrow counties, Oregon. Unpublished dissertation. State College of Washington, Pullman. 166 pp.
- Reid, M. S., L. S. Engelking, and P. S. Bourgeron. 1994. Rare plant communities of the conterminous United States, Western Region. Pages 305-620 in: D. H. Grossman, K. L. Goodin, and C. L. Reuss, editors. Rare plant communities of the conterminous United States, an initial survey. The Nature Conservancy, Arlington, VA.
- Roughton, R. D. 1966. Age structure of browse populations. Unpublished thesis, Colorado State University, Fort Collins. 154 pp.
- Roughton, R. D. 1972. Shrub age structures on a mule deer winter range in Colorado. Ecology 53(4):615-625.
- Sawyer, J. O., T. Keeler-Wolf, and J. Evens. 2009. A manual of California vegetation. Second edition. California Native Plant Society, Sacramento CA. 1300 pp.
- Sawyer, J. O., and T. Keeler-Wolf. 1995. A manual of California vegetation. California Native Plant Society, Sacramento. 471 pp.
- Tisdale, E. W. 1947. The grasslands of the southern interior of British Columbia. Ecology 28(4):346-382.
- Tweit, S., and K. Houston. 1980. Grassland and shrubland habitat types of the Shoshone National Forest. USDA Forest Service, Rocky Mountain Region, Shoshone National Forest.
- Volland, L. A. 1976. Plant communities of the central Oregon pumice zone. USDA Forest Service R-6 Area Guide 4-2. Pacific Northwest Region, Portland, OR. 113 pp.
- WNHP [Washington Natural Heritage Program]. 2018. Unpublished data files. Washington Natural Heritage Program, Department of Natural Resources, Olympia, WA.
- Wasser, C. H., and K. Hess. 1982. The habitat types of Region II. USDA Forest Service: A synthesis. Final report prepared for USDA Forest Service, Rocky Mountain Forest and Range Experiment Station, Fort Collins, CO. 140 pp.