
Natural Resources
Conservation Service
Ecological site F043AD900MT
Lower Subalpine Coniferous Subalpine fir/bride's bonnet
Last updated: 5/06/2025
Accessed: 05/19/2025
General information
Provisional. A provisional ecological site description has undergone quality control and quality assurance review. It contains a working state and transition model and enough information to identify the ecological site.
MLRA notes
Major Land Resource Area (MLRA): 043A–Northern Rocky Mountains
This ecological site currently resides in the Major Land Resource Area (MLRA) 43A Northern Rocky Mountains. The area of MLRA 43A is expansive and is further divided into Land Resource Units (LRU). A detailed description of MLRA 43A can be found at:
https://www.nrcs.usda.gov/wps/portal/nrcs/detail/soils/ref/?cid=nrcs142p2_053624
Major Land Resource Area (MLRA): 043A–Northern Rocky Mountains
This MLRA is located in Montana (43 percent), Idaho (34 percent), and Washington (23 percent). It makes up about 31,435 square miles (81,460 square kilometers). It has no large cities or towns. It has many national forests, including the Okanogan, Colville, Kootenai, Lolo, Flathead, Coeur d’Alene, St. Joe, Clearwater, and Kaniksu National Forests.
This MLRA is in the Northern Rocky Mountains Province of the Rocky Mountain System. It is characterized by rugged, glaciated mountains; thrust- and block-faulted mountains; and hills and valleys. Steep-gradient rivers have cut deep canyons. Natural and manmade lakes are common.
The major Hydrologic Unit Areas (identified by four-digit numbers) that make up this MLRA are: Kootenai-Pend Oreille-Spokane (1701), 67 percent; Upper Columbia (1702), 18 percent; and Lower Snake (1706), 15 percent. Numerous rivers originate in or flow through this area, including, the Sanpoil, Columbia, Pend Oreille, Kootenai, St. Joe, Thompson, and Flathead Rivers.
This area is underlain primarily by stacked slabs of layered sedimentary or metasedimentary bedrock. The bedrock formations range from Precambrian to Cretaceous in age. The rocks consist of shale, sandstone, siltstone, limestone, argillite, quartzite, gneiss, schist, dolomite, basalt, and granite. The formations have been faulted and stacked into a series of imbricate slabs by regional tectonic activity. Pleistocene glaciers carved a rugged landscape that includes sculpted hills and narrow valleys filled with till and outwash. Continental glaciation over road the landscape in the northern half of the MLRA while glaciation in the southern half was confined to montane settings.
The average annual precipitation is 25 to 60 inches (635 to 1,525 millimeters) in most of this area, but it is as much as 113 inches (2,870 millimeters) in the mountains and is 10 to 15 inches (255 to 380 millimeters) in the western part of the area. Summers are dry. Most of the precipitation during fall, winter, and spring is snow. The average annual temperature is 32 to 51 degrees F (0 to 11 degrees C) in most of the area, decreasing with elevation. In most of the area, the freeze-free period averages 140 days and ranges from 65 to 215 days. It is longest in the low valleys of Washington, and it decreases in length with elevation. Freezing temperatures occur every month of the year on high mountains, and some peaks have a continuous cover of snow and ice.
The dominant soil orders in this MLRA are Andisols, Inceptisols, and Alfisols. Many of the soils are influenced by Mount Mazama ash deposits. The soils in the area have a frigid or cryic soil temperature regime; have an ustic, xeric, or udic soil moisture regime; and dominantly have mixed mineralogy. They are shallow to very deep, are very poorly drained to well-drained, and have most of the soil texture classes. The soils at the lower elevations include Udivitrands, Vitrixerands and Haplustalfs. The soils at the higher elevations include Dystrocryepts, Eutrocryepts, Vitricryands , and Haplocryalfs. Cryorthents, Cryepts, and areas of rock outcrop are on ridges and peaks above timberline
This area is in the northern part of the Northern Rocky Mountains. Grand fir, Douglas-fir, western red cedar, western hemlock, western larch, lodgepole pine, subalpine fir, ponderosa pine, whitebark pine, and western white pine are the dominant overstory species, depending on precipitation, temperature, elevation, and landform aspect. The understory vegetation varies, also depending on climatic and landform factors. Some of the major wildlife species in this area are white-tailed deer, mule deer, elk, moose, black bear, grizzly bear, coyote, fox, and grouse. Fish, mostly in the trout and salmon families, are abundant in streams, rivers, and lakes.
More than one-half of this area is federally owned and administered by the U.S. Department of Agriculture, Forest Service. Much of the privately-owned land is controlled by large commercial timber companies. The forested areas are used for wildlife habitat, recreation, watershed, livestock grazing, and timber production. Meadows provide summer grazing for livestock and big game animals. Less than three percent of the area is cropland.
LRU notes
LRU D-RATTLESNAKE, MISSION MOUNTAINS, AND BOB MARSHALL.
The landscape is mountains, and the landforms are mountain slopes, alpine ridges and cirquelands and valley floors. The area includes the Whitefish, Swan and Flathead mountains. The Whitefish/Swan Mtns. are block faulted mountain ranges are formed from argillite, siltite and dolomite and strongly shaped by alpine glaciation. Glacial till covers much of the landscape. Some volcanic ash deposits. Flathead Mtns. are thrust faulted mountains that formed from shale, sandstone, limestone and conglomerate. These mountains have been strongly shaped by alpine glaciation. The elevation ranges from 2900 feet to 8000 feet for the Whitefish and Swan mountains and 3680 feet to 8500 feet for the Flathead mountains. The drainage density for both areas is moderate. The geology is mainly Belt series (Missoula group and others) and alluvium in the valley areas. There is Cambrian in the eastern portion of and Glacial geology throughout, Kootenai in the northeastern portion and Tertiary geology in the northern portion of the area. The soils of the mountains are predominantly till with volcanic ash and in the valley areas alluvium or outwash. The soil temperature regime is mainly cryic, and the soil moisture regime is mainly udic. The mean annual precipitation ranges from 50 inches to 70 inches with about 80 percent falling as snow for the entire area. Lakes occur in glacial cirques and in glacial valleys in the Whitefish and Swan mountains and a few in the glacial cirque basins in the Flathead mountains. The main vegetation for the area is Douglas fir forest types and western spruce-fir forest types. This LRU is predominantly all federally owned lands including Bob Marshall Wilderness, Flathead N.F., Great Bear Wilderness and Flathead Indian Reservation. There are small areas of Lolo N.F., Mission Mountain Wilderness, National Bison Range and Scapegoat Wilderness. Borders Swan River NWR, Glacier N.P. and the Lewis and Clark N.F. Land cover is predominantly conifer xeric-mesic and mesic-wet type, recently burned, Alpine sparse and barren and harvested forest areas. Specifically, in the Whitefish and Swan mountains, the land use is predominantly rural and suburban development and some timber harvest. In the Flathead mountains, the land use is predominantly wilderness and therefore human disturbances are minor. The primary natural disturbances are fire, insects and windthrow.
Classification relationships
This is related to the EPA land classification framework of: Level 3- 41 Canadian Rockies. Specifically, it includes Levels 41c, 41e, minor 41b (tiny amount of 41d, 15l and 15a).
This area is related predominantly to the USFS Province M333Cb Whitefish/Swan Mtns., and M333Ce Flathead Thrust Faulted Mtns. This LRU is roughly two-thirds Province Cb and a third Province Ce.
Ecological site concept
It is in cool, moist mid-elevations that span the lower subalpine zone. This ecological site is found on back, foot and toeslope positions, on mountain slope and stream terrace landforms, on slopes less than forty percent, at elevations ranging 1,300 to 1400 meters. Subalpine fir (Abies lasiocarpa) and Engelmann spruce (Picea engelmannii) are the dominant overstory species with co-occurring Douglas-fir (Pseudotsuga menziesii) and lodgepole pine (Pinus contorta). The main understory species are the medium sized shrub Rocky Mountain Maple, the mid height shrub Thinleaf huckleberry (Vaccinium membranaceum) with an understory of wild sarsaparilla, threelaf foamflower and queencup bead lily (Clintonia uniflora). Soils associated with this Ecological Site are very deep, well drained or somewhat excessively drained and have subsoils with abundant rock fragments. There is no flooding or ponding on this site. The parent material is colluvium, alluvium or glacial till from metasedimentary rock. If volcanic ash is found in these soils, it originates from the eruption of Mount Mazama (Crater Lake, Oregon) and is apparent in the soil profile as a surface mantle or series of layers in the upper part of the soil profile. Volcanic ash has properties that provide important additions to the subsurface soils that occur below the ash cap. Low bulk density, typically less rock fragments, and high water holding capacity increase the storage of water near the surface in soils with volcanic ash. In Soil Taxonomy, these soils classify primarily as loamy-skeletal Inceptisols soil order and fine-loamy Alfisols. Some areas may have Alfisols (with a volcanic ash cap).
Table 1. Dominant plant species
Tree |
(1) Abies lasiocarpa |
---|---|
Shrub |
Not specified |
Herbaceous |
(1) Clintonia uniflora |
Physiographic features
It is in cool, moist mid-elevations that span the lower subalpine zone. This ecological site is found on back, foot and toeslope positions, on mountain slope and stream terrace landforms, on slopes less than forty percent, at elevations ranging from 1,300 to 1400 meters.
Table 2. Representative physiographic features
Landforms |
(1)
Mountains
> Hillslope
(2) Mountain valleys or canyons > Stream terrace |
---|---|
Elevation | 4,265 – 4,600 ft |
Slope | 40% |
Aspect | W, NW, N, NE, E, SE, S, SW |
Climatic features
Climate may vary by general locations, but the data below is a summary based on climate station data from sites close to the proximity of the ecological site.
Table 3. Representative climatic features
Frost-free period (characteristic range) | 11-78 days |
---|---|
Freeze-free period (characteristic range) | 68-123 days |
Precipitation total (characteristic range) | 16-20 in |
Frost-free period (actual range) | 7-86 days |
Freeze-free period (actual range) | 64-128 days |
Precipitation total (actual range) | 13-23 in |
Frost-free period (average) | 46 days |
Freeze-free period (average) | 100 days |
Precipitation total (average) | 18 in |
Figure 1. Monthly precipitation range
Figure 2. Monthly minimum temperature range
Figure 3. Monthly maximum temperature range
Figure 4. Monthly average minimum and maximum temperature
Figure 5. Annual precipitation pattern
Figure 6. Annual average temperature pattern
Climate stations used
-
(1) LINDBERGH LAKE [USC00245043], Seeley Lake, MT
-
(2) SEELEY LAKE RS [USC00247448], Bonner, MT
-
(3) OVANDO 9 SSE [USC00246304], Helmville, MT
-
(4) LINCOLN RS [USC00245040], Lincoln, MT
-
(5) GIBSON DAM [USC00243489], Augusta, MT
-
(6) ROGERS PASS 9 NNE [USC00247159], Wolf Creek, MT
Influencing water features
There are no water features with this ecological site.
Wetland description
There are no wetlands with this ecological site.
Soil features
Soils associated with this Ecological Site are very deep, well drained and have subsoils with abundant rock fragments. There is no flooding or ponding on this site. The parent material is colluvium, alluvium or glacial till from metasedimentary rock. If volcanic ash is found in these soils, it originates from the eruption of Mount Mazama (Crater Lake, Oregon) and is apparent in the soil profile as a surface mantle or series of layers in the upper part of the soil profile. Volcanic ash has properties that provide important additions to the subsurface soils that occur below the ash cap. Low bulk density, typically less rock fragments, and high-water holding capacity increase the storage of water near the surface in soils with volcanic ash. In Soil Taxonomy, these soils classify primarily as loamy-skeletal Inceptisols soil order and fine-loamy Alfisols.
For more information on soil taxonomy, please follow this link:
http://http://www.nrcs.usda.gov/wps/portal/nrcs/detail/soils/survey/class/?cid=nrcs142p2_053580
Table 4. Representative soil features
Parent material |
(1)
Alluvium
–
metasedimentary rock
(2) Colluvium – metasedimentary rock (3) Till – metasedimentary rock |
---|---|
Surface texture |
(1) Ashy |
Family particle size |
(1) Fine-loamy |
Drainage class | Well drained |
Soil depth | 60 in |
Surface fragment cover <=3" | 35% |
Surface fragment cover >3" | 35% |
Subsurface fragment volume <=3" (Depth not specified) |
35% |
Subsurface fragment volume >3" (Depth not specified) |
35% |
Ecological dynamics
State and transition model
More interactive model formats are also available.
View Interactive Models
Click on state and transition labels to scroll to the respective text
State 2 submodel, plant communities
State 3 submodel, plant communities
State 1
Historic Reference Western White Pine at high levels throughout region
Community 1.1
Reference
Western White Pine/ Subalpine fir-Engelmann spruce/Rocky Mountain maple-rusty menziesia-thimbleberry/twinflower/queencup beadlily-liverwort wintergreen-broadleaf arnica. Structure: Multistory with small gap dynamics. Rare phase due to disturbance rotations (fire interval).
Community 1.2
Post fire disturbance phase
Seedlings of western white pine, western larch and lodgepole pine. Structure: short, young seedlings of various species throughout, resprouting shrubs, single story short stand. Time: 0 to 50 years post fire.
Community 1.3
Competitive Exclusion Phase
The forest overstory is a densely spaced stand of pole sized trees, predominantly western white pine and western larch. There are other tree species in lesser abundance including subalpine fir, Engelmann spruce and Douglas fir. The understory can be diminished in abundance due to low light levels at the ground resulting from the shading of the thick overstory. Structure: dense single aged stand Time spent in this phase is 50 to 150 years.
Community 1.4
Vertical Differentiation phase
Mature trees in the overstory with some small pockets of blow down or other disturbance that leads to more light reaching the forest floor allowing for tree regeneration and higher abundance of understory species. Western white pine is dominant with other species in lesser amounts including subalpine fir, Engelmann spruce and Douglas fir and western larch. Understory is diverse and abundant in the open pockets, but may be diminished if the overstory is dense, single stand. Structure: single story stand transitioning to a multi-storied stand with pockets of blow down and regeneration. Time: 140 years to centuries.
Community 1.5
Mature, multi-story stand with some small pockets phase
Multi-story forest overstory dominated by western white pine with less other tree species including western larch, subalpine fir, Douglas fir and Engelmann spruce. Structure: single story stand transitioning to a multi-storied stand with pockets of blow down and regeneration. Understory is diverse and abundant in the open pockets, but may be diminished if the overstory is dense, single stand. Structure: Multi-storied stand with scattered pockets. Time: 140 years to centuries.
State 2
Current Potential Without Western White Pine to a large degree
Community 2.1
Reference community phase
COMMUNITY PHASE 2.1: Subalpine fir-Engelmann spruce/Rocky Mountain maple-rusty menziesia-thimbleberry/twinflower/queencup beadlily-liverwort wintergreen-broadleaf arnica Structure: multistory with small gap dynamics The overstory is dominated by Subalpine fir and Engelmann spruce with small gap dynamics in which small numbers of trees are dead and conifer regeneration is infilling. Overstory canopy cover ranges 40-60%. The understory is very lush, diverse and multi-storied (canopy cover dataset of 4 sites). Species occurring with high frequency of occurrence and high-moderate cover include the tall shrubs Rocky mountain maple and rusty menziesia and thimbleberry. The next lower shrub layer includes twinflower. The lowest layer includes grasses and forbs including broadleaf arnica, mountain brome, liverwort wintergreen, queencup beadlily, threeleaf foamflower and darkwoods violet. This is substantiated by 4 sites with canopy cover and production data, and two sites with foliar cover data. The community is multi-storied with tall trees ranging 80 to 120 feet tall. The understory is multi-layered with shrubs 76-101 cm (30-40 inches) tall including rusty menziesia, thimbleberry. The next layer is 51-76 cm (20-30 inches) tall and includes ribes species, western meadowrue and mountain brome. Then there is a layer 25-51 cm (10-20 inches) tall including white spirea and common snowberry. The lowest layer is comprised of forbs and grasses about 15-25 cm (6-10 inches) tall including liverwort wintergreen, broadleaf arnica, queencup beadlily and diverse forbs. At these higher elevations both tree species are slow growing and infill can take several decades, sustaining the multistory structure of this community. The presence of root rot pockets can shift the composition of this community away from its host species. The understory of this community is multistoried as well with the mid-sized shrubs rocky mountain maple, thinleaf huckleberry and thimbleberry in clumps, and the herbaceous layer varied but with wild sarsaparilla, threeleaf foamflower and queencup bead lily apparent. This ecological site must have a presence of queencup bead lily and sometimes this is dominant. At this phase Armillaria root rot and defoliation by Western Spruce budworm can be a threat.
Dominant plant species
-
subalpine fir (Abies lasiocarpa), tree
-
Engelmann spruce (Picea engelmannii), tree
-
rusty menziesia (Menziesia ferruginea), shrub
-
thimbleberry (Rubus parviflorus), shrub
-
Rocky Mountain maple (Acer glabrum), shrub
-
twinflower (Linnaea borealis), shrub
-
bride's bonnet (Clintonia uniflora), other herbaceous
-
liverleaf wintergreen (Pyrola asarifolia), other herbaceous
-
broadleaf arnica (Arnica latifolia), other herbaceous
Figure 7. Annual production by plant type (representative values) or group (midpoint values)
Table 5. Soil surface cover
Tree basal cover | 0-10% |
---|---|
Shrub/vine/liana basal cover | 0-5% |
Grass/grasslike basal cover | 0-2% |
Forb basal cover | 0-2% |
Non-vascular plants | 0-5% |
Biological crusts | 0-1% |
Litter | 60-90% |
Surface fragments >0.25" and <=3" | 0-5% |
Surface fragments >3" | 0-5% |
Bedrock | 0% |
Water | 0% |
Bare ground | 0-10% |
Table 6. Canopy structure (% cover)
Height Above Ground (ft) | Tree | Shrub/Vine | Grass/ Grasslike |
Forb |
---|---|---|---|---|
<0.5 | 0-5% | 0-20% | 0-10% | 0-10% |
>0.5 <= 1 | 0-5% | 0-20% | 0-10% | 0-10% |
>1 <= 2 | 0-5% | 0-20% | 0-10% | 0-10% |
>2 <= 4.5 | 0-5% | 0-10% | – | – |
>4.5 <= 13 | 0-10% | 0-5% | – | – |
>13 <= 40 | 0-10% | – | – | – |
>40 <= 80 | 20-40% | – | – | – |
>80 <= 120 | 40-60% | – | – | – |
>120 | 0-10% | – | – | – |
Community 2.2
Multistoried stand with small pockets of blow down and regeneration
COMMUNITY PHASE 2.2: Subalpine fir-Engelmann spruce (western larch-Douglas-fir)/thinleaf huckleberry-Pacific yew- rusty menziesia/Oregon boxwood-mountain lover/broadleaf arnica-beargrass Structure: mosaic of mature overstory and regenerating openings Community Phase 1.2 retains some areas that resemble Community Phase1.1, but it also contains moderate-sized (2-5 acres) openings. The canopy cover averages 60 percent. Subalpine fir and Engelmann spruce are both host to organisms causing root rot and heart rot, and with windthrow can cause large pockets of overstory mortality. These areas may take decades to become reforested, resulting in either patches of shrubs or seral species such as western larch and Douglas-fir. As the organisms slowly die off due to a lack of host trees, subalpine fir and Engelmann spruce will re-colonize these areas. This community can be prone to Armillaria root rot and western spruce budworm on fir.
Dominant plant species
-
subalpine fir (Abies lasiocarpa), tree
-
Engelmann spruce (Picea engelmannii), tree
-
western larch (Larix occidentalis), tree
-
Douglas-fir (Pseudotsuga menziesii), tree
-
thinleaf huckleberry (Vaccinium membranaceum), shrub
-
Pacific yew (Taxus brevifolia), shrub
-
rusty menziesia (Menziesia ferruginea), shrub
-
Oregon boxleaf (Paxistima myrsinites), shrub
-
broadleaf arnica (Arnica latifolia), other herbaceous
-
common beargrass (Xerophyllum tenax), other herbaceous
Community 2.3
Post fire disturbance community phase
COMMUNITY PHASE 2.3 white spirea/Fireweed-Canada goldenrod-alpine leafybract aster Structure: patchy clumps of regeneration, single story Community Phase1.3 is a forest in the stand initiation phase, possibly with scattered remnant mature trees; the composition of the seedlings depends upon the natural seed sources available. The canopy cover is generally less than 10 percent as a mixture of conifers including Douglas-fir, lodgepole pine, western larch, Engelmann spruce and subalpine fir. If serotinous lodgepole seedbank is present, this species will dominate the area.
Dominant plant species
-
white spirea (Spiraea betulifolia), shrub
-
Canada goldenrod (Solidago canadensis), other herbaceous
-
alpine leafybract aster (Symphyotrichum foliaceum), other herbaceous
-
fireweed (Chamerion angustifolium), other herbaceous
Community 2.4
Competitive Exclusion community phase
COMMUNITY PHASE 2.4: Lodgepole pine (Douglas-fir-subalpine fir-Engelmann spruce)/ceanothus/white spirea-prickly rose/Ladyfern-pinegrass-beargrass Structure: dense single story Community Phase 2.4 is a forest in the competitive exclusion phase, possibly with scattered remnant mature trees; individual trees compete for the available water and nutrients. The canopy cover ranges from 50-80 percent. Canopy closure is very high within the areas successfully reforested, leading eventually to a diminished graminoid community, but also providing protection for those species which do well in the shade, such as prince’s pine and queencup beadlily. This community is more tolerant of Armillaria root rot due to forest stand composition, but is prone to defoliation by western spruce budworm on fir.
Dominant plant species
-
lodgepole pine (Pinus contorta), tree
-
Douglas-fir (Pseudotsuga menziesii), tree
-
Engelmann spruce (Picea engelmannii), tree
-
subalpine fir (Abies lasiocarpa), tree
-
snowbrush ceanothus (Ceanothus velutinus), shrub
-
white spirea (Spiraea betulifolia), shrub
-
rose (Rosa), shrub
-
pinegrass (Calamagrostis rubescens), grass
-
common ladyfern (Athyrium filix-femina), other herbaceous
-
common beargrass (Xerophyllum tenax), other herbaceous
Community 2.5
Mature single story stand with small pockets of blow down and regeneration.
COMMUNITY PHASE 2.5: Subalpine fir-Engelmann spruce (western larch-Douglas-fir)/Sitka alder/Rocky Mountain maple-rusty menziesia/wild sarsaparilla-twinflower-queencup beadlily Structure: single story with few small openings Community Phase 2.5 is a maturing forest which is starting to differentiate vertically. The canopy cover ranges from averages 50 percent of mixed conifer species including subalpine fir, Engelmann spruce, Douglas fir and western larch. Individual trees are dying due to insects, disease, competition, or windthrow, allowing some sunlight to reach the forest floor. This allows for an increase in the understory, as well as some pockets of overstory tree species regeneration. This community is prone to Armillaria root rot and western spruce budworm on fir. The understory is lush, diverse and multi-storied. Species with high frequency of occurrence and moderate to high canopy cover (21 sites dataset) include the tall shrubs Sitka alder and Rocky mountain maple, the medium statured shrubs thinleaf huckleberry, thimbleberry and white spirea and Oregon boxleaf. The lowest layer includes queencup beadlily, threeleaf foamflower, western meadowrue, darkwoods violet, twinflower, heartleaf arnica, wild sarspirella and Pacific oakfern.
State 3
Root Rot
Community 3.1
Additional community tables
Table 7. Community 2.1 plant community composition
Group | Common name | Symbol | Scientific name | Annual production (lb/acre) | Foliar cover (%) | |
---|---|---|---|---|---|---|
Grass/Grasslike
|
||||||
1 | – | |||||
pinegrass | CARU | Calamagrostis rubescens | 0–200 | 0–60 | ||
mountain brome | BRMA4 | Bromus marginatus | – | 0–2 | ||
Forb
|
||||||
2 | – | |||||
heartleaf arnica | ARCO9 | Arnica cordifolia | 0–500 | 0–15 | ||
common beargrass | XETE | Xerophyllum tenax | 0–300 | 0–15 | ||
common ladyfern | ATFI | Athyrium filix-femina | 0–220 | – | ||
liverleaf wintergreen | PYAS | Pyrola asarifolia | 0–200 | – | ||
alpine leafybract aster | SYFO2 | Symphyotrichum foliaceum | 0–150 | – | ||
western meadow-rue | THOC | Thalictrum occidentale | 0–100 | 0–2 | ||
white hawkweed | HIAL2 | Hieracium albiflorum | 0–85 | 0–5 | ||
fireweed | CHAN9 | Chamerion angustifolium | 0–80 | 0–15 | ||
broadleaf arnica | ARLA8 | Arnica latifolia | 0–60 | 0–15 | ||
western rattlesnake plantain | GOOB2 | Goodyera oblongifolia | 0–50 | – | ||
greenflowered wintergreen | PYCH | Pyrola chlorantha | 0–20 | – | ||
bride's bonnet | CLUN2 | Clintonia uniflora | 0–15 | 0–2 | ||
darkwoods violet | VIOR | Viola orbiculata | 0–10 | – | ||
western pearly everlasting | ANMA | Anaphalis margaritacea | – | 0–2 | ||
sweetcicely | OSBE | Osmorhiza berteroi | – | 0–2 | ||
roughfruit fairybells | PRTR4 | Prosartes trachycarpa | – | 0–2 | ||
Shrub/Vine
|
||||||
3 | – | |||||
white spirea | SPBE2 | Spiraea betulifolia | 0–300 | 0–50 | ||
thimbleberry | RUPA | Rubus parviflorus | 0–300 | 0–5 | ||
thinleaf huckleberry | VAME | Vaccinium membranaceum | 0–100 | 0–5 | ||
creeping barberry | MARE11 | Mahonia repens | 0–80 | 0–15 | ||
rusty menziesia | MEFE | Menziesia ferruginea | 0–60 | – | ||
pipsissewa | CHUM | Chimaphila umbellata | 0–15 | – | ||
common snowberry | SYAL | Symphoricarpos albus | – | 0–2 |
Table 8. Community 2.1 forest overstory composition
Common name | Symbol | Scientific name | Nativity | Height (ft) | Canopy cover (%) | Diameter (in) | Basal area (square ft/acre) |
---|---|---|---|---|---|---|---|
Tree
|
|||||||
subalpine fir | ABLA | Abies lasiocarpa | Native | 60–80 | 20–40 | 15–25 | – |
subalpine fir | ABLA | Abies lasiocarpa | Native | 80–120 | 20–40 | 20–35 | – |
Engelmann spruce | PIEN | Picea engelmannii | Native | 60–120 | 20–40 | 15–35 | – |
Douglas-fir | PSME | Pseudotsuga menziesii | Native | 60–120 | 1–15 | 15–35 | – |
western larch | LAOC | Larix occidentalis | Native | 60–120 | 3–10 | 15–35 | – |
Table 9. Community 2.1 forest understory composition
Common name | Symbol | Scientific name | Nativity | Height (ft) | Canopy cover (%) | |
---|---|---|---|---|---|---|
Grass/grass-like (Graminoids)
|
||||||
pinegrass | CARU | Calamagrostis rubescens | Native | – | 0–2 | |
sedge | CAREX | Carex | Native | – | 0–1 | |
blue wildrye | ELGL | Elymus glaucus | Native | – | 0–1 | |
horsetail | EQUIS | Equisetum | Native | – | 0–1 | |
mountain brome | BRMA4 | Bromus marginatus | Native | – | 0–1 | |
Hitchcock's smooth woodrush | LUGLH | Luzula glabrata var. hitchcockii | Native | – | 0–1 | |
Sitka valerian | VASI | Valeriana sitchensis | Native | – | 0–1 | |
fescue | VULPI | Vulpia | Native | – | 0–1 | |
Forb/Herb
|
||||||
heartleaf arnica | ARCO9 | Arnica cordifolia | Native | – | 0–75 | |
common cowparsnip | HEMA80 | Heracleum maximum | Native | – | 0–35 | |
bride's bonnet | CLUN2 | Clintonia uniflora | Native | – | 0–30 | |
liverleaf wintergreen | PYAS | Pyrola asarifolia | Native | – | 0–20 | |
western meadow-rue | THOC | Thalictrum occidentale | Native | – | 0–20 | |
broadleaf arnica | ARLA8 | Arnica latifolia | Native | – | 0–15 | |
common beargrass | XETE | Xerophyllum tenax | Native | – | 0–10 | |
common snowberry | SYAL | Symphoricarpos albus | Native | – | 0–10 | |
western showy aster | EUCO36 | Eurybia conspicua | Native | – | 0–5 | |
arrowleaf ragwort | SETR | Senecio triangularis | Native | – | 0–5 | |
miterwort | MITEL | Mitella | Native | – | 0–5 | |
darkwoods violet | VIOR | Viola orbiculata | Native | – | 0–5 | |
fivestamen miterwort | MIPE | Mitella pentandra | Native | – | 0–3 | |
common mullein | VETH | Verbascum thapsus | Introduced | – | 0–3 | |
bracted lousewort | PEBR | Pedicularis bracteosa | Native | – | 0–2 | |
sickletop lousewort | PERA | Pedicularis racemosa | Native | – | 0–2 | |
yellow avalanche-lily | ERGR9 | Erythronium grandiflorum | Native | – | 0–1 | |
strawberry | FRAGA | Fragaria | Native | – | 0–1 | |
northern bedstraw | GABO2 | Galium boreale | Native | – | 0–1 | |
sticky purple geranium | GEVI2 | Geranium viscosissimum | Native | – | 0–1 | |
western rattlesnake plantain | GOOB2 | Goodyera oblongifolia | Native | – | 0–1 | |
green false hellebore | VEVI | Veratrum viride | Native | – | 0–1 | |
violet | VIOLA | Viola | Native | – | 0–1 | |
trillium | TRILL | Trillium | Native | – | 0–1 | |
feathery false lily of the valley | MARA7 | Maianthemum racemosum | Native | – | 0–1 | |
beardtongue | PENST | Penstemon | Native | – | 0–1 | |
greenflowered wintergreen | PYCH | Pyrola chlorantha | Native | – | 0–1 | |
ragwort | SENEC | Senecio | Native | – | 0–1 | |
claspleaf twistedstalk | STAM2 | Streptopus amplexifolius | Native | – | 0–1 | |
thistle | CIRSI | Cirsium | Native | – | 0–1 | |
starry false lily of the valley | MAST4 | Maianthemum stellatum | Native | – | 0–1 | |
Fern/fern ally
|
||||||
rusty menziesia | MEFE | Menziesia ferruginea | Native | – | 0–40 | |
twinflower | LIBO3 | Linnaea borealis | Native | – | 0–30 | |
common ladyfern | ATFI | Athyrium filix-femina | Native | – | 0–10 | |
Pacific oakfern | GYDI2 | Gymnocarpium disjunctum | Native | – | 0–1 | |
Shrub/Subshrub
|
||||||
Rocky Mountain maple | ACGL | Acer glabrum | Native | – | 0–30 | |
thimbleberry | RUPA | Rubus parviflorus | Native | – | 0–25 | |
russet buffaloberry | SHCA | Shepherdia canadensis | Native | – | 0–10 | |
Saskatoon serviceberry | AMAL2 | Amelanchier alnifolia | Native | – | 0–10 | |
thinleaf huckleberry | VAME | Vaccinium membranaceum | Native | – | 0–10 | |
creeping barberry | MARE11 | Mahonia repens | Native | – | 0–5 | |
Oregon boxleaf | PAMY | Paxistima myrsinites | Native | – | 0–3 | |
pipsissewa | CHUM | Chimaphila umbellata | Native | – | 0–3 | |
Utah honeysuckle | LOUT2 | Lonicera utahensis | Native | – | 0–2 | |
common juniper | JUCO6 | Juniperus communis | Native | – | 0–1 | |
Pacific yew | TABR2 | Taxus brevifolia | Native | – | 0–1 | |
grouse whortleberry | VASC | Vaccinium scoparium | Native | – | 0–1 |
Table 10. Community 2.2 forest overstory composition
Common name | Symbol | Scientific name | Nativity | Height (ft) | Canopy cover (%) | Diameter (in) | Basal area (square ft/acre) |
---|---|---|---|---|---|---|---|
Tree
|
|||||||
subalpine fir | ABLA | Abies lasiocarpa | Native | 60–120 | 20–40 | – | – |
western larch | LAOC | Larix occidentalis | Native | 60–120 | 10–30 | – | – |
Engelmann spruce | PIEN | Picea engelmannii | Native | 60–120 | 10–30 | – | – |
Douglas-fir | PSME | Pseudotsuga menziesii | Native | 60–120 | 10–30 | – | – |
Table 11. Community 2.2 forest understory composition
Common name | Symbol | Scientific name | Nativity | Height (ft) | Canopy cover (%) | |
---|---|---|---|---|---|---|
Grass/grass-like (Graminoids)
|
||||||
mountain brome | BRMA4 | Bromus marginatus | Native | – | 0–1 | |
horsetail | EQUIS | Equisetum | Native | – | 0–1 | |
Forb/Herb
|
||||||
broadleaf arnica | ARLA8 | Arnica latifolia | Native | – | 0–20 | |
common beargrass | XETE | Xerophyllum tenax | Native | – | 0–10 | |
heartleaf arnica | ARCO9 | Arnica cordifolia | Native | – | 0–5 | |
bride's bonnet | CLUN2 | Clintonia uniflora | Native | – | 0–5 | |
sweetcicely | OSBE | Osmorhiza berteroi | Native | – | 0–2 | |
northern bedstraw | GABO2 | Galium boreale | Native | – | 0–1 | |
western meadow-rue | THOC | Thalictrum occidentale | Native | – | 0–1 | |
violet | VIOLA | Viola | Native | – | 0–1 | |
Alberta beardtongue | PEAL11 | Penstemon albertinus | Native | – | 0–1 | |
roughfruit fairybells | PRTR4 | Prosartes trachycarpa | Native | – | 0–1 | |
greenflowered wintergreen | PYCH | Pyrola chlorantha | Native | – | 0–1 | |
vetch | VICIA | Vicia | Native | – | 0–1 | |
Shrub/Subshrub
|
||||||
rusty menziesia | MEFE | Menziesia ferruginea | Native | – | 0–20 | |
creeping barberry | MARE11 | Mahonia repens | Native | – | 0–15 | |
Rocky Mountain maple | ACGL | Acer glabrum | Native | – | 0–15 | |
twinflower | LIBO3 | Linnaea borealis | Native | – | 0–10 | |
Oregon boxleaf | PAMY | Paxistima myrsinites | Native | – | 0–10 | |
Pacific yew | TABR2 | Taxus brevifolia | Native | – | 0–10 | |
thinleaf huckleberry | VAME | Vaccinium membranaceum | Native | – | 0–10 | |
Saskatoon serviceberry | AMAL2 | Amelanchier alnifolia | Native | – | 0–10 | |
white spirea | SPBE2 | Spiraea betulifolia | Native | – | 0–10 | |
thimbleberry | RUPA | Rubus parviflorus | Native | – | 0–10 | |
twinberry honeysuckle | LOIN5 | Lonicera involucrata | Native | – | 0–5 | |
russet buffaloberry | SHCA | Shepherdia canadensis | Native | – | 0–5 | |
rose | ROSA5 | Rosa | Native | – | 0–5 | |
common snowberry | SYAL | Symphoricarpos albus | Native | – | 0–5 | |
pipsissewa | CHUM | Chimaphila umbellata | Native | – | 0–5 | |
dwarf bilberry | VACE | Vaccinium cespitosum | Native | – | 0–2 |
Table 12. Community 2.3 forest understory composition
Common name | Symbol | Scientific name | Nativity | Height (ft) | Canopy cover (%) | |
---|---|---|---|---|---|---|
Grass/grass-like (Graminoids)
|
||||||
bluejoint | CACA4 | Calamagrostis canadensis | Native | – | 0–5 | |
northwestern sedge | CACO11 | Carex concinnoides | Native | – | 0–3 | |
tufted hairgrass | DECE | Deschampsia cespitosa | Native | – | 0–3 | |
Geyer's sedge | CAGE2 | Carex geyeri | Native | – | 0–1 | |
Forb/Herb
|
||||||
fireweed | CHAN9 | Chamerion angustifolium | Native | – | 0–45 | |
Canada goldenrod | SOCA6 | Solidago canadensis | Native | – | 0–15 | |
alpine leafybract aster | SYFO2 | Symphyotrichum foliaceum | Native | – | 0–10 | |
heartleaf arnica | ARCO9 | Arnica cordifolia | Native | – | 0–5 | |
western pearly everlasting | ANMA | Anaphalis margaritacea | Native | – | 0–3 | |
Canada thistle | CIAR4 | Cirsium arvense | Native | – | 0–2 | |
common beargrass | XETE | Xerophyllum tenax | Native | – | 0–1 | |
Fern/fern ally
|
||||||
kinnikinnick | ARUV | Arctostaphylos uva-ursi | Native | – | 0–1 | |
Shrub/Subshrub
|
||||||
white spirea | SPBE2 | Spiraea betulifolia | Native | – | 0–10 | |
Sitka alder | ALVIS | Alnus viridis ssp. sinuata | Native | – | 0–5 | |
Utah honeysuckle | LOUT2 | Lonicera utahensis | Native | – | 0–2 | |
grouse whortleberry | VASC | Vaccinium scoparium | Native | – | 0–2 | |
creeping barberry | MARE11 | Mahonia repens | Native | – | 0–1 | |
red elderberry | SARA2 | Sambucus racemosa | Native | – | 0–1 |
Table 13. Community 2.4 forest overstory composition
Common name | Symbol | Scientific name | Nativity | Height (ft) | Canopy cover (%) | Diameter (in) | Basal area (square ft/acre) |
---|---|---|---|---|---|---|---|
Tree
|
|||||||
lodgepole pine | PICO | Pinus contorta | Native | – | 0–50 | – | – |
Douglas-fir | PSME | Pseudotsuga menziesii | Native | – | 0–20 | – | – |
Engelmann spruce | PIEN | Picea engelmannii | Native | – | 0–5 | – | – |
subalpine fir | ABLA | Abies lasiocarpa | Native | – | 0–5 | – | – |
Table 14. Community 2.4 forest understory composition
Common name | Symbol | Scientific name | Nativity | Height (ft) | Canopy cover (%) | |
---|---|---|---|---|---|---|
Grass/grass-like (Graminoids)
|
||||||
pinegrass | CARU | Calamagrostis rubescens | Native | – | 0–35 | |
Geyer's sedge | CAGE2 | Carex geyeri | Native | – | 0–3 | |
blue wildrye | ELGL | Elymus glaucus | Native | – | 0–3 | |
mountain brome | BRMA4 | Bromus marginatus | Native | – | 0–3 | |
northwestern sedge | CACO11 | Carex concinnoides | Native | – | 0–2 | |
sedge | CAREX | Carex | Native | – | 0–1 | |
Indian paintbrush | CASTI2 | Castilleja | Native | – | 0–1 | |
Forb/Herb
|
||||||
common beargrass | XETE | Xerophyllum tenax | Native | – | 0–30 | |
fireweed | CHAN9 | Chamerion angustifolium | Native | – | 0–10 | |
western meadow-rue | THOC | Thalictrum occidentale | Native | – | 0–10 | |
broadleaf arnica | ARLA8 | Arnica latifolia | Native | – | 0–10 | |
western pearly everlasting | ANMA | Anaphalis margaritacea | Native | – | 0–5 | |
violet | VIOLA | Viola | Native | – | 0–5 | |
bride's bonnet | CLUN2 | Clintonia uniflora | Native | – | 0–5 | |
Scouler's willow | SASC | Salix scouleriana | Native | – | 0–5 | |
Virginia strawberry | FRVI | Fragaria virginiana | Native | – | 0–5 | |
sweetcicely | OSBE | Osmorhiza berteroi | Native | – | 0–3 | |
feathery false lily of the valley | MARA7 | Maianthemum racemosum | Native | – | 0–3 | |
alpine leafybract aster | SYFO2 | Symphyotrichum foliaceum | Native | – | 0–3 | |
roughfruit fairybells | PRTR4 | Prosartes trachycarpa | Native | – | 0–3 | |
California oatgrass | DACA3 | Danthonia californica | Native | – | 0–3 | |
heartleaf arnica | ARCO9 | Arnica cordifolia | Native | – | 0–3 | |
white hawkweed | HIAL2 | Hieracium albiflorum | Native | – | 0–3 | |
common yarrow | ACMI2 | Achillea millefolium | Native | – | 0–2 | |
strawberry | FRAGA | Fragaria | Native | – | 0–2 | |
raceme pussytoes | ANRA | Antennaria racemosa | Native | – | 0–2 | |
American trailplant | ADBI | Adenocaulon bicolor | Native | – | 0–2 | |
nettleleaf giant hyssop | AGUR | Agastache urticifolia | Native | – | 0–2 | |
western stoneseed | LIRU4 | Lithospermum ruderale | Native | – | 0–2 | |
arrowleaf ragwort | SETR | Senecio triangularis | Native | – | 0–2 | |
Canada goldenrod | SOCA6 | Solidago canadensis | Native | – | 0–2 | |
ragwort | SENEC | Senecio | Native | – | 0–1 | |
common dandelion | TAOF | Taraxacum officinale | Introduced | – | 0–1 | |
northern bedstraw | GABO2 | Galium boreale | Native | – | 0–1 | |
streambank wild hollyhock | ILRI | Iliamna rivularis | Native | – | 0–1 | |
wild sarsaparilla | ARNU2 | Aralia nudicaulis | Native | – | 0–1 | |
aster | ASTER | Aster | Native | – | 0–1 | |
hookedspur violet | VIAD | Viola adunca | Native | – | 0–1 | |
pointedtip mariposa lily | CAAP | Calochortus apiculatus | Native | – | 0–1 | |
darkwoods violet | VIOR | Viola orbiculata | Native | – | 0–1 | |
bluebell bellflower | CARO2 | Campanula rotundifolia | Native | – | 0–1 | |
Canada thistle | CIAR4 | Cirsium arvense | Native | – | 0–1 | |
fragrant bedstraw | GATR3 | Galium triflorum | Native | – | 0–1 | |
western rattlesnake plantain | GOOB2 | Goodyera oblongifolia | Native | – | 0–1 | |
Scouler's woollyweed | HISC2 | Hieracium scouleri | Native | – | 0–1 | |
western sweetroot | OSOC | Osmorhiza occidentalis | Native | – | 0–1 | |
sickletop lousewort | PERA | Pedicularis racemosa | Native | – | 0–1 | |
eastern pasqueflower | PUPA5 | Pulsatilla patens | Native | – | 0–1 | |
liverleaf wintergreen | PYAS | Pyrola asarifolia | Native | – | 0–1 | |
Fern/fern ally
|
||||||
common ladyfern | ATFI | Athyrium filix-femina | Native | – | 0–25 | |
prickly currant | RILA | Ribes lacustre | Native | – | 0–1 | |
Shrub/Subshrub
|
||||||
grouse whortleberry | VASC | Vaccinium scoparium | Native | – | 0–20 | |
thinleaf huckleberry | VAME | Vaccinium membranaceum | Native | – | 0–20 | |
snowbrush ceanothus | CEVE | Ceanothus velutinus | Native | – | 0–20 | |
white spirea | SPBE2 | Spiraea betulifolia | Native | – | 0–20 | |
kinnikinnick | ARUV | Arctostaphylos uva-ursi | Native | – | 0–15 | |
common snowberry | SYAL | Symphoricarpos albus | Native | – | 0–15 | |
Rocky Mountain maple | ACGL | Acer glabrum | Native | – | 0–10 | |
Saskatoon serviceberry | AMAL2 | Amelanchier alnifolia | Native | – | 0–10 | |
thimbleberry | RUPA | Rubus parviflorus | Native | – | 0–10 | |
russet buffaloberry | SHCA | Shepherdia canadensis | Native | – | 0–10 | |
rose | ROSA5 | Rosa | Native | – | 0–10 | |
creeping barberry | MARE11 | Mahonia repens | Native | – | 0–10 | |
Oregon boxleaf | PAMY | Paxistima myrsinites | Native | – | 0–5 | |
pipsissewa | CHUM | Chimaphila umbellata | Native | – | 0–5 | |
twinflower | LIBO3 | Linnaea borealis | Native | – | 0–3 | |
western mountain ash | SOSI2 | Sorbus sitchensis | Native | – | 0–2 | |
dwarf bilberry | VACE | Vaccinium cespitosum | Native | – | 0–2 | |
rusty menziesia | MEFE | Menziesia ferruginea | Native | – | 0–2 | |
common juniper | JUCO6 | Juniperus communis | Native | – | 0–1 | |
strawberryleaf raspberry | RUPE | Rubus pedatus | Native | – | 0–1 | |
Utah honeysuckle | LOUT2 | Lonicera utahensis | Native | – | 0–1 | |
Sitka alder | ALVIS | Alnus viridis ssp. sinuata | Native | – | 0–1 |
Interpretations
Supporting information
Contributors
Stephanie Shoemaker
Approval
Kirt Walstad, 5/06/2025
Acknowledgments
There has been a range of detailees and volunteers to assist in collecting data within this project area.
Rangeland health reference sheet
Interpreting Indicators of Rangeland Health is a qualitative assessment protocol used to determine ecosystem condition based on benchmark characteristics described in the Reference Sheet. A suite of 17 (or more) indicators are typically considered in an assessment. The ecological site(s) representative of an assessment location must be known prior to applying the protocol and must be verified based on soils and climate. Current plant community cannot be used to identify the ecological site.
Author(s)/participant(s) | |
---|---|
Contact for lead author | |
Date | 05/13/2025 |
Approved by | Kirt Walstad |
Approval date | |
Composition (Indicators 10 and 12) based on | Annual Production |
Indicators
-
Number and extent of rills:
-
Presence of water flow patterns:
-
Number and height of erosional pedestals or terracettes:
-
Bare ground from Ecological Site Description or other studies (rock, litter, lichen, moss, plant canopy are not bare ground):
-
Number of gullies and erosion associated with gullies:
-
Extent of wind scoured, blowouts and/or depositional areas:
-
Amount of litter movement (describe size and distance expected to travel):
-
Soil surface (top few mm) resistance to erosion (stability values are averages - most sites will show a range of values):
-
Soil surface structure and SOM content (include type of structure and A-horizon color and thickness):
-
Effect of community phase composition (relative proportion of different functional groups) and spatial distribution on infiltration and runoff:
-
Presence and thickness of compaction layer (usually none; describe soil profile features which may be mistaken for compaction on this site):
-
Functional/Structural Groups (list in order of descending dominance by above-ground annual-production or live foliar cover using symbols: >>, >, = to indicate much greater than, greater than, and equal to):
Dominant:
Sub-dominant:
Other:
Additional:
-
Amount of plant mortality and decadence (include which functional groups are expected to show mortality or decadence):
-
Average percent litter cover (%) and depth ( in):
-
Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
-
Potential invasive (including noxious) species (native and non-native). List species which BOTH characterize degraded states and have the potential to become a dominant or co-dominant species on the ecological site if their future establishment and growth is not actively controlled by management interventions. Species that become dominant for only one to several years (e.g., short-term response to drought or wildfire) are not invasive plants. Note that unlike other indicators, we are describing what is NOT expected in the reference state for the ecological site:
-
Perennial plant reproductive capability:
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