Print Report

CEGL001304 Atriplex confertifolia / Pleuraphis jamesii Shrubland

Type Concept Sentence: No Data Available


Common (Translated Scientific) Name: Shadscale Saltbush / James'' Galleta Shrubland

Colloquial Name: No Data Available

Hierarchy Level:  Association

Type Concept: This widespread western shrubland association is reported from the southwestern Great Plains, Colorado Plateau, Great Basin, Columbia Plateau and possibly Mojave Desert mountains. This shrubland association is characterized by a sparse to open canopy (5-25% cover) of short shrubs dominated by Atriplex confertifolia with a sparse to moderate graminoid layer dominated by Pleuraphis jamesii. It includes sparsely vegetated stands with as little as 1-2% cover of shrubs and 1% cover of Pleuraphis jamesii. Total vegetation cover is widely variable (2-70%). Associated shrubs include Artemisia bigelovii, Artemisia tridentata ssp. wyomingensis, Atriplex canescens, Chrysothamnus viscidiflorus, Coleogyne ramosissima, Ephedra torreyana, Ericameria nauseosa, Grayia spinosa, Gutierrezia sarothrae, Krascheninnikovia lanata, Opuntia polyacantha, Picrothamnus desertorum, Sarcobatus vermiculatus, Suaeda calceoliformis, Suaeda moquinii, and Tetradymia canescens depending on substrate. Amphipappus fremontii, Ambrosia dumosa, and Lycium pallidum occur in the Mojave Desert. Other graminoids include Achnatherum hymenoides, Sporobolus cryptandrus, and Elymus elymoides on sandy sites and Bouteloua gracilis and Sporobolus airoides on fine-textured soil. Forbs generally have low cover and may include Sphaeralcea grossulariifolia, Eriogonum inflatum, and species of Chaenactis, Lappula, Phacelia, Plantago, and Chenopodium. Introduced species such as Bromus tectorum and Salsola kali are common on some sites. It occurs in a variety of habitats and can be found on two distinct substrates: coarse-textured, non-saline soils derived from sandstone or gravel or deep, fine-textured, alkaline, often saline soils derived from shale. Stands with coarse-textured soils tend to be on slopes, while those with fine-textured soils tend to be on low, relatively flat positions in the landscape (valley bottoms, basins, etc.). The common trait of these different substrates is that they are very dry either because of low precipitation or because of high internal plant moisture stress from soil salinity. The unvegetated surface is composed largely of bare soil, gravel, and large or small rocks.

Diagnostic Characteristics: No Data Available

Rationale for Nominal Species or Physiognomic Features: No Data Available

Classification Comments: This widespread shrubland association is only defined by the codominance of Atriplex confertifolia and Pleuraphis jamesii. Stands are found in different regions (primarily the Great Basin and Colorado Plateau with extensions into the Mojave Desert (possibly), southwestern Wyoming and in disjunct stands in the southwestern Great Plains), in different environments (clay bottomlands, dunes, desert mountains) and with different associated species. This association will likely need to be subdivided as more classification information becomes available. Stands of this association with a sparse herbaceous layer are similar to ~Atriplex confertifolia Great Basin Shrubland (CEGL001294)$$. Sparse stands included in the concept of this association are very similar to ~Atriplex confertifolia Sparse Shrubland (CEGL003830)$$. More classification work is needed to clarify differences.

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

Physiognomy and Structure: No Data Available

Floristics: This shadscale shrubland association is characterized by an open canopy (5-25% cover) of short shrubs dominated by Atriplex confertifolia with a sparse to moderate graminoid layer dominated by Pleuraphis jamesii. This association includes sparsely vegetated stands with as little as 1-2% cover of shrubs and 1% cover of Pleuraphis jamesii. Total vegetation cover is widely variable (2-70% in sampled stands). Associated shrubs include Artemisia bigelovii, Artemisia tridentata ssp. wyomingensis, Atriplex canescens, Chrysothamnus viscidiflorus, Coleogyne ramosissima, Ephedra torreyana, Ephedra viridis, Ericameria nauseosa, Eriogonum microthecum, Grayia spinosa, Gutierrezia microcephala, Gutierrezia sarothrae, Krascheninnikovia lanata, Lycium pallidum, Picrothamnus desertorum, Psorothamnus fremontii, Sarcobatus vermiculatus, Suaeda calceoliformis, Suaeda moquinii (= Suaeda fruticosa), and Tetradymia canescens depending on substrate. Amphipappus fremontii, Ambrosia dumosa, and Lycium pallidum occur in the Mojave Desert. Succulents may include Echinocereus triglochidiatus, Opuntia polyacantha var. erinacea (= Opuntia erinacea), Opuntia polyacantha var. polyacantha, Sclerocactus whipplei, and Yucca harrimaniae. Rarely, tree and tall-shrub species are present and may include Juniperus osteosperma and Fraxinus anomala. If other Atriplex species are present, they do not dominate the canopy. The herbaceous layer is often sparse, less than 10% total cover, but ranges up to 30% cover. Other graminoids include Achnatherum hymenoides, Sporobolus cryptandrus, Sporobolus flexuosus, and Elymus elymoides on sandy sites and Bouteloua gracilis, Poa fendleriana, Poa secunda, and Sporobolus airoides on finer-textured soil. Forbs generally have low cover and moderate diversity and may include Astragalus nuttallianus, Calochortus flexuosus, Calochortus nuttallii, Cirsium sp., Cryptantha flavoculata, Cymopterus purpurascens, Descurainia pinnata, Eriogonum inflatum, Eriogonum lonchophyllum, Lappula occidentalis, Lepidium montanum, Oenothera pallida, Phacelia crenulata, Plantago patagonica, Platyschkuhria integrifolia, Rumex hymenosepalus, Senecio integerrimus, Sphaeralcea coccinea, Sphaeralcea grossulariifolia, and species of Chaenactis, Cryptantha, Phacelia, and Chenopodium. Introduced annual species such as Bromus rubens, Bromus tectorum, Erodium cicutarium, and Salsola kali are common on some sites. Biological soil crusts are variable, with some stands having very little, but cover can be as high as 80%.

Dynamics:  Ecological processes vary with landscape type, but droughty conditions are important in shaping and maintaining this association. In wetter year, trees such as Juniperus osteosperma may invade.

Environmental Description:  Elevation ranges from 1066 to 1951 m in the Colorado Plateau. It is found on two distinct substrates: coarse-textured (rocky or sandy), non-saline soils derived from sandstone or gravel, or deep fine-textured, poorly drained, alkaline, often-saline soils derived from shale or shale-derived alluvium. Sites with coarse-textured soils include gravel and cobble outcrops, ridges, mesa escarpments, talus slopes, alluvial fans, mountain and hillslopes, canyonsides, benches and along toeslopes of river bluffs. Fine-textured soil sites include canyon bottoms, plains, alluvial flats, floodplains and basins. Stands with coarse-textured soils can be on flat to moderately steep slopes, while stands with fine-textured soils are typically on flat to gently sloping sites. The common trait of these different substrates is that they are very dry either because of low precipitation (15-23 cm annually) or because of high internal plant moisture stress from soil salinity. The unvegetated surface is composed largely of bare soil, gravel, and large or small rocks. Cryptogamic crusts and mosses are important in some stands. Parent materials are variable and in the Colorado Plateau include sandstones and shale of the Burro Canyon Formation, Cedar Mountain Formation, Chinle Formation, Elephant Canyon Formation, Entrada Formation, Kayenta Formation sandstone, Mancos shale, Morrison Formation, Moenkopi Formation, and Wingate Formation typically deposited as alluvium or eolian sand.

Geographic Range: This widespread shrubland association occurs throughout much of the southern intermountain western U.S. and is reported from the Great Basin, Colorado Plateau, and possibly Mojave Desert mountains and east into the disjunct stands in the southwestern Great Plains.

Nations: US

States/Provinces:  AZ, CA?, CO, NM, NV, UT, WY




Confidence Level: High

Confidence Level Comments: No Data Available

Grank: G3G5

Greasons: No Data Available


Concept Lineage: No Data Available

Predecessors: No Data Available

Obsolete Names: No Data Available

Obsolete Parents: No Data Available

Synonomy: >< Atripletum confertifolae association (Ibrahim et al. 1972) [Total canopy cover was sparse (10%) with 4.6% ATCO and 3.3% PLJA.]
= Atriplex confertifolia / Pleuraphis jamesii Shrubland (Von Loh 2000)
= Atriplex confertifolia/Hilaria jamesii Habitat Type (West and Ibrahim 1968) [See note from Ibrahim et al. 1972.]
>< Atriplex confertifolia Association in the Mixed Shrub Zone (Annable 1985)
= Atriplex confertifolia Plant Community (Branson et al. 1976)
= Atriplex confertifolia cover type (Tuhy and MacMahon 1988) [Includes both Atriplex confertifolia/Hilaria jamesii community type and Atriplex confertifolia/Hilaria jamesii- Stipa hymenoides community type.]
= Atriplex-Tetradymia Association (Graham 1937)
>< Gutierrezia sarothrae - Atriplex confertifolia (Potter et al. 1985) [Occurs on top of Mancos Shale knolls.]
>< Frontier Sandstone (Welsh 1957) [Occurs on northern exposures on sand and on southern aspects at base of slope.]
>< Mat Atriplex-Hilaria Community (Dastrup 1963) [This community is codominated by Atriplex confertifolia and Atriplex corrugata.]
= Shadscale/grass (Harper and Jaynes 1986)

Concept Author(s): K.A. Schulz

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

Acknowledgements: No Data Available

Version Date: 12-06-16

  • Annable, C. R. 1985. Vegetation and flora of the Funeral Mountains, Death Valley National Monument. California-Nevada Cooperative National Park Resources Studies Unit, National Park Service/University of Nevada Contribution 016/07. Las Vegas, NV. 188 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.
  • Branson, F. A., R. F. Miller, and I. S. McQueen. 1976. Moisture relationships in twelve northern desert shrub communities near Grand Junction, Colorado. Ecology 57:1104-1124.
  • Branson, F. A., and J. B. Owen. 1970. Plant cover, runoff, and sediment yield relationships on Mancos shale in western Colorado. Water Resources Research 6:783-790.
  • 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/]
  • Campbell, V. O. 1977. Certain edaphic and biotic factors affecting vegetation in the shadscale community of the Kaiparowitz area. Unpublished thesis, Brigham Young University, Provo, UT. 59 pp.
  • 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.
  • 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.
  • Coles, J., D. Cogan, D. Salas, A. Wight, G. Wakefield, J. Von Loh, and A. Evenden. 2008a. Vegetation classification and mapping project report, Dinosaur National Monument. Natural Resource Technical Report NPS/NCPN/NRTR-2008/112. National Park Service, Fort Collins, CO. 814 pp.
  • Dastrup, B. C. 1963. Vegetational changes of the Uinta Basin since settlement. Unpublished thesis, Brigham Young University, Provo, UT. 118 pp.
  • Graham, E. H. 1937. Botanical studies in the Uinta Basin of Utah and Colorado. Annals of the Carnegie Museum 26:28-432.
  • Harper, K. T., and R. A. Jaynes. 1986. Some edaphic and compositional characteristics of Artemisia tridentata and associated plant communities in southeastern Utah. Pages 265-272 in: E. D. McArthur and B. L. Welch, compilers. Proceedings-Symposium on the Biology of Artemisia and Chrysothamnus, 9-13 July, Provo, UT. General Technical Report INT-200. USDA Forest Service, Intermountain Research Station, Ogden, UT.
  • Ibrahim, K. M., N. E. West, and D. L. Goodwin. 1972. Phytosociological characteristics of perennial Atriplex-dominated vegetation of southeastern Utah. Vegetatio 24:13-22.
  • Lusby, G. C., G. T. Turner, J. R. Thompson, and V. H. Reid. 1963. Hydrologic and biotic characteristics of grazed and ungrazed watersheds of the Badger Wash Basin in western Colorado, 1953-1958. U.S. Geological Survey Water-Supply Paper 1532-B.
  • 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.
  • Potter, L. D., R. C. Reynolds, Jr., and E. T. Louderbough. 1985. Mancos shale and plant community relationships: Analysis of shale, soil, and vegetation transects. Journal of Arid Environments 9:147-165.
  • 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.
  • Salas, D., L. Floyd-Hanna, and D. Hanna. 2011. Vegetation classification and mapping project report: Chaco Culture National Historical Park. Natural Resource Technical Report NPS/SCPN/NRTR--2011/452. National Park Service, Fort Collins, CO. 142 pp.
  • Singh, T., and N. E. West. 1971. Comparison of some multivariate analyses of perennial Atriplex vegetation in southeastern Utah. Vegetatio 23(5-6):289-313.
  • Soil Conservation Service. 1978. Range site descriptions for Colorado. Technical Guide, Section II-E. USDA Soil Conservation Service, Colorado State Office, Denver.
  • 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.
  • Thomas, K. A., M. L. McTeague, L. Ogden, K. Schulz, T. Fancher, R. Waltermire, and A. Cully. 2010. Vegetation classification and distribution mapping report: Canyon de Chelly National Monument. National Resource Technical Report NPS/SCPN/NRTR-2010/306. National Park Service, Fort Collins, CO. 338 pp.
  • Tuhy, J. S., and J. A. MacMahon. 1988. Vegetation and relict communities of Glen Canyon National Recreation Area. Unpublished final report prepared for USDI National Park Service, Rocky Mountain Region, Lakewood, CO. Utah State University, Logan. 299 pp.
  • USBOR [U.S. Bureau of Reclamation]. 1976. Flora and terrestrial vertebrate studies of the Grand Valley, Colorado. Pages 56-85 and 283-354 in: Final report to the U.S. Bureau of Reclamation by Ecology Consultants, Inc., Fort Collins, CO.
  • Von Loh, J. 2000. Draft local descriptions of the vegetation associations of Ouray National Wildlife Refuge. USGS Bureau of Reclamation, Remote Sensing and GIS Group, Denver Federal Center, Denver.
  • Von Loh, J., D. Cogan, K. Schulz, D. Crawford, T. Meyer, J. Pennell, and M. Pucherelli. 2002. USGS-USFWS Vegetation Mapping Program, Ouray National Wildlife Refuge, Utah. USDI Bureau of Reclamation, Remote Sensing and GIS Group, Technical Memorandum 8260-02-03. Denver Federal Center, Denver, CO. 225 pp.
  • Von Loh, J., G. Wakefield, A. Wight, A. Evenden, and J. Coles. 2008. Vegetation classification and mapping project report, Hovenweep National Monument. Natural Resource Report NPS/NCPN/NRTR--2008/092. National Park Service, Fort Collins, CO. 328 pp.
  • Von Loh, J., K. Landgraf, A. Evenden, T. Owens, S. Blauer, and M. Reid. 2007. Vegetation classification and mapping project report, Colorado National Monument. Natural Resource Report NPS/NCPN/NRTR--2007/061. National Park Service, Fort Collins, CO. 564 pp.
  • WNDD [Wyoming Natural Diversity Database]. No date. Unpublished data on file. Wyoming Natural Diversity Database, University of Wyoming, Laramie, WY.
  • Welsh, S. L. 1957. An ecological survey of the vegetation of the Dinosaur National Monument, Utah. Unpublished thesis, Brigham Young University, Provo, UT. 86 pp.
  • West, N. E., and K. I. Ibrahim. 1968. Soil-vegetation relationships in the shadscale zone of southeastern Utah. Ecology 49(3):445-456.
  • Western Ecology Working Group of NatureServe. No date. International Ecological Classification Standard: International Vegetation Classification. Terrestrial Vegetation. NatureServe, Boulder, CO.