Search Field Guide
Advanced Search
MT Gov Logo
Montana Field Guide

Montana Field Guides

Lowland - Montane Shrubland
Global Name: Central Rocky Mountain Montane-Foothill Shrubland

Global Rank: G4G5
State Rank: S4S5

(see reason below)

External Links




State Rank Reason
This habitat has been altered or lost due to development, grazing practices, invasive species and severe wildfires. However, the type is still relatively common, widespread and resilient.
 

General Description
This National Vegetation Classification Group is dominated by deciduous shrubs at low to mid elevations. It is found in the foothills and montane zone of all mountainous areas across the state. Patches sizes are generally small. These communities occur in relatively warm, dry, upland habitats and may be dominated or co-dominated by the following shrubs: Serviceberry (Amelanchier alnifolia), Ninebark (Physocarpus malvaceus), Chokecherry (Prunus virginiana), Oceanspray (Holodiscus discolor), Bitter Cherry (Prunus emarginata), Smooth Sumac (Rhus glabra), Skunkbush Sumac (Rhus trilobata), Woods' Rose (Rosa woodsii), and Common Snowberry (Symphoricarpos albus). These shrublands often occur below treeline, within the matrix of surrounding low-elevation grasslands and sagebrush shrublands. They also occur in the ponderosa pine and Douglas-fir zones, but rarely up into the subalpine zone, where they are restricted to warm, dry sites and southerly exposures. Trees if present within the community are widely scattered. These shrublands occur on all aspects. These communities also develop near talus slopes as garlands, at the heads of dry drainages, and toeslopes in the moist shrub-steppe and steppe zones. Fire, flooding and erosion all impact these shrublands, but they typically will persist on sites for long periods.

This group incorporates the Rocky Mountain Lower Montane-Foothill Shrubland Ecological System as well as a portion of the Rocky Mountain Montane-Foothill Deciduous Shrubland Ecological System.

Diagnostic Characteristics
Shrublands; Foothills and Montane Zones; Rocky Mountain and Western Great Plains Regions; Upland Sites; Warm, Dry Settings

Typical Dominants: Serviceberry (Amelanchier alnifolia), Ninebark (Physocarpus malvaceus), Chokecherry (Prunus virginiana), Oceanspray (Holodiscus discolor), Bitter Cherry (Prunus emarginata), Smooth Sumac (Rhus glabra), Skunkbush Sumac (Rhus trilobata), Woods' Rose (Rosa woodsii), and Common Snowberry (Symphoricarpos albus)

Similar Systems

Range
In Montana, these communities occur throughout the mountainous portions of the state, both east and west of the Continental Divide. It extends as far east as the Little Rockies, the Little Snowies and the Wolf Mtns in Big Horn County.

In MT, G272 occurs within these Level III Ecoregions: 15 (Northern Rockies), 16 (Idaho Batholith), 17 (Middle Rockies), 41 (Canadian Rockies) and western portions of 42 (Northwestern Glaciated Plains) and 43 (Northwestern Great Plains).

In Montana, G272 occurs within these Major Land Resource Areas: 43A - Northern Rocky Mountains and 43B - Central Rocky Mountains, 44A - Northern Rocky Mountain Valleys, and 46 - Northern and Central Rocky Mountain Foothills.

Density and Distribution
Based on 2025 land cover layer. Grid on map is based on USGS 7.5 minute quadrangle map boundaries.



Mapped Distribution by County
Beaverhead, Big Horn, Blaine, Broadwater, Carbon, Cascade, Chouteau, Deer Lodge, Fergus, Flathead, Gallatin, Glacier, Golden Valley, Granite, Hill, Jefferson, Judith Basin, Lake, Lewis and Clark, Liberty, Lincoln, Madison, Meagher, Mineral, Missoula, Musselshell, Park, Petroleum, Phillips, Pondera, Powell, Ravalli, Sanders, Silver Bow, Stillwater, Sweet Grass, Teton, Toole, Wheatland, Yellowstone
Based on 2025 land cover layer.

Spatial Pattern
Small Patch and Large Patch

Environment
These shrubland communities occur in relatively warm, dry, upland habitats in the foothills and the montane zone of all mountainous areas across the state. Rarely, they may reach into the lower subalpine zone on warm and dry, southerly aspects. At low and mid elevations they may be found on all aspects and on slopes of various steepness, though mostly on gentle to moderate slopes. Patch sizes are generally small and dictated in part by topographic breaks, slope steepness and drainage patterns.

Vegetation
These communities occur in relatively warm, dry, upland habitats and may be dominated or co-dominated by the following shrubs: Serviceberry (Amelanchier alnifolia), Ninebark (Physocarpus malvaceus), Chokecherry (Prunus virginiana), Oceanspray (Holodiscus discolor), Bitter Cherry (Prunus emarginata), Smooth Sumac (Rhus glabra), Skunkbush Sumac (Rhus trilobata), Woods' Rose (Rosa woodsii), and Common Snowberry (Symphoricarpos albus). Sumac communities occupy the hottest and driest sites of the shrublands within this Group.

Graminoids and forbs are common undergrowth in these shrublands. Grasses and sedges that may be abundant vary by geography and by the specific plant association but may include Purple Three-awn (Aristida purpurea), Pinegrass (Calamagrostis rubescens), Geyer's Sedge (Carex geyeri), Rough Fescue (Festuca campestris), Idaho fescue (Festuca idahoensis), Prairie Junegrass (Koeleria macrantha), Sandberg Bluegrass (Poa secunda), and Bluebunch wheatgrass (Elymus spicatus). Cheatgrass (Bromus tectorum) and Timothy (Phleum pratense) are common introduced grasses in some of these shrublands. Species of forbs in these communities vary widely by geography and by the specific plant association. Invasive forbs are also widespread in these communities and occasionally abundant, especially Spotted knapweed (Centaurea stoebe).

Adjacent or nearby riparian communities may be dominated or co-dominated by some of the same shrub species but can be distinguished in part by occurring in riparian or floodplain zones and by the presence of other riparian shrubs or riparian herbaceous species. These riparian shrub communities are part of G526 Lowland - Foothill Riparian Shrubland.

In Montana, this group is represented by 3 Alliances and 6 Associations within the National Vegetation Classification. Additional types may exist in the state.

National Vegetation Classification

Download the complete NVC hierarchy for Montana

TT4 B04 Temperate-Boreal Grassland and Shrubland
TT4.b S58 Temperate Grassland and Shrubland
TT4.b1 F116 Temperate Lowland-Montane Grassland and Shrubland
TT4.b1.Ne D022 Western North American Grassland and Shrubland
TT4.b1.Ne.2 M548 Central Rocky Mountain Montane-Foothill Shrubland
TT4.b1.Ne.2.a G272 Central Rocky Mountain Montane-Foothill Shrubland
A3936 Ceanothus velutinus Shrubland Alliance
CEGL002167 Ceanothus velutinus Shrubland
CEGL008236 Salix scouleriana - Acer glabrum - (Ceanothus velutinus) Shrubland
CEGL008241 Ceanothus velutinus - Amelanchier alnifolia / Maianthemum racemosum Shrubland
A3963 Amelanchier alnifolia Montane-Foothill Shrubland Alliance
CEGL001065 Amelanchier alnifolia / Pseudoroegneria spicata - Bunchgrass Shrubland
CEGL005885 Amelanchier alnifolia / (Mixed Grass, Forb) Shrubland
A3964 Rhus glabra - Rhus trilobata Central Rockies Montane-Foothill Dry Shrubland Alliance
CEGL001120 Rhus trilobata / Pseudoroegneria spicata Shrub Grassland
CEGL001505 Rhus trilobata / Festuca idahoensis Shrub Grassland
A3975 Physocarpus malvaceus - Symphoricarpos albus Mesic Shrubland Alliance
CEGL005606 Prunus virginiana / Leymus cinereus Shrubland
CEGL005890 Symphoricarpos albus Shrubland
A4096 Dasiphora fruticosa / Festuca campestris - Festuca idahoensis Shrub-steppe Alliance
CEGL001502 Dasiphora fruticosa / Festuca idahoensis Shrub Grassland
CEGL001503 Dasiphora fruticosa / Festuca campestris Shrub Grassland
View more information on the NVC standard in Montana
*Disclaimer: Some Alliances and Associations are considered provisional. Some require further documentation to verify their occurrence in the state and some may be modified or deleted in future revisions after collection of additional data and information.

Dynamic Processes
Fires may be frequent in these low elevation, dry shrublands. Most of the common shrubs of these communities have the potential to re-sprout following all but the most severe fires. As a result, fires help to perpetuate some of these shrublands not only by the ability to resprout but also by reducing conifer encroachment. Establishment of new shrubland communities following severe fire is possible on some formerly forested sites. Once established, these communities generally persist for long periods of time.

Management
Information on the management of these communities is lacking at this time.

Restoration Considerations
Information on restoration considerations of these communities is lacking at this time.

Species Associated with this Community
  • How Lists Were Created and Suggested Uses and Limitations
    Animal Species Associations
    Please note that while all vertebrate species have been systematically associated with vegetation communities, only a handful of invertebrate species have been associated with vegetation communities and invertebrates lists for each vegetation community should be regarded as incomplete. Animal species associations with natural vegetation communities that they regularly breed or overwinter in or migrate through were made by:
    1. Using personal observations and reviewing literature that summarize the breeding, overwintering, or migratory habitat requirements of each species (Dobkin 1992, Hart et al. 1998, Hutto and Young 1999, Maxell 2000, Werner et al. 2004, Adams 2003, and Foresman 2012);
    2. Evaluating structural characteristics and distribution of each vegetation community relative to the species' range and habitat requirements;
    3. Examining the observation records for each species in the state-wide point observation database associated with each vegetation community;
    4. Calculating the percentage of observations associated with each vegetation community relative to the percent of Montana covered by each vegetation community to get a measure of "observations versus availability of habitat".
    Species that breed in Montana were only evaluated for breeding habitat use. Species that only overwinter in Montana were only evaluated for overwintering habitat use. Species that only migrate through Montana were only evaluated for migratory habitat use. In general, species are listed as associated with a vegetation community if it contains structural characteristics known to be used by the species. However, species are not listed as associated with a vegetation community if we found no support in the literature for the species’ use of structural characteristics of the community even if point observations were associated with it. If you have any questions or comments on animal species associations with vegetation communities, please contact the Montana Natural Heritage Program's Senior Zoologist.

    Plant Species Associations
    Please note that while diagnostic, dominant, or codominant vascular plant species for a vegetation community have been systematically assigned to those communities and vascular plant Species of Concern were systematically evaluated for their associations with vegetation communities, the majority of Montana’s vascular plant species have not been evaluated for their associations with vegetation communities and no attempt has been made to associate non-vascular plants, fungi, or lichens with vegetation communities. Plant species associations with natural vegetation communities were made in a manner similar to that described above for animals, but with review of Lesica et al. (2022) and specimen collection data from the Consortium of Pacific Northwest Herbaria. If you have any questions or comments on plant species associations with vegetation communities, please contact the Montana Natural Heritage Program's Program Botanist.

    Suggested Uses and Limitations
    Species associations with vegetation communities should be used to generate potential lists of species that may occupy broader landscapes for the purposes of landscape-level planning. These potential lists of species should not be used in place of documented occurrences of species or predicted habitat suitability models (this information can be requested at: https://mtnhp.mt.gov/requests/), or systematic surveys for species and onsite evaluations of habitat by trained biologists. Users of this information should be aware that the land cover data used to generate species associations is based on satellite imagery from 2016 and was only intended to be used at broader landscape scales. Land cover mapping accuracy is particularly problematic when the vegetation communities occur as small patches or where the land cover types have been altered over the past decade. Thus, particular caution should be used when using the associations in assessments of smaller areas (e.g., evaluations of public land survey sections). Finally, although a species may be associated with a particular vegetation community within its known geographic range, portions of that vegetation community may occur outside of the species' known geographic range.

    Literature Cited
    • Adams, R.A. 2003. Bats of the Rocky Mountain West; natural history, ecology, and conservation. Boulder, CO: University Press of Colorado. 289 p.
    • Consortium of Pacific Northwest Herbaria. https://www.pnwherbaria.org/ Last accessed May 30, 2025.
    • Dobkin, D. S. 1992. Neotropical migrant land birds in the Northern Rockies and Great Plains. USDA Forest Service, Northern Region. Publication No. R1-93-34. Missoula, MT.
    • Foresman, K.R. 2012. Mammals of Montana. Second edition. Mountain Press Publishing, Missoula, Montana. 429 pp.
    • Hart, M.M., W.A. Williams, P.C. Thornton, K.P. McLaughlin, C.M. Tobalske, B.A. Maxell, D.P. Hendricks, C.R. Peterson, and R.L. Redmond. 1998. Montana atlas of terrestrial vertebrates. Montana Cooperative Wildlife Research Unit, University of Montana, Missoula, MT. 1302 p.
    • Hutto, R.L. and J.S. Young. 1999. Habitat relationships of landbirds in the Northern Region, USDA Forest Service, Rocky Mountain Research Station RMRS-GTR-32. 72 p.
    • Lesica P., M. Lavin, and P.F. Stickney. 2022. Manual of vascular plants, 2nd Edition. Brit Press. 779 p.
    • Maxell, B.A. 2000. Management of Montana's amphibians: a review of factors that may present a risk to population viability and accounts on the identification, distribution, taxonomy, habitat use, natural history, and the status and conservation of individual species. Report to U.S. Forest Service Region 1. Missoula, MT: Wildlife Biology Program, University of Montana. 161 p.
    • Werner, J.K., B.A. Maxell, P. Hendricks, and D. Flath. 2004. Amphibians and reptiles of Montana. Missoula, MT: Mountain Press Publishing Company. 262 p.

Original Concept Authors
M.S. Reid and K.A. Schulz 2015

Montana Version Authors
S. Mincemoyer, T. Luna and L. Vance

Version Date
12/5/2024


References
  • Additional ReferencesLegend:   View Online Publication
    Do you know of a citation we're missing?
    • Mueggler, W. F. and W. L. Stewart. 1980. Grassland and shrubland habitat types of western Montana. USDA Forest Service Gen. Tech. Rep. INT-66, Intermountain Forest and Range Exp. Sta., Ogden, Utah. 154 pp.
    • Shiflet, T. N., editor. 1994. Rangeland cover types of the United States. Society for Range Management. Denver, CO. 152 pp.
Login Logout
Citation for data on this website:
Lowland - Montane Shrubland.  Montana Field Guide.  Retrieved on , from