Natural Resources
Conservation Service
Ecological site R009XY035OR
Cold South
17-24 PZ
Last updated: 5/05/2025
Accessed: 04/17/2026
-
Search
Major Land Resource Area or ecological site by name and/or ID.
PreviousSectionsNextGeneral 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.
Click to explore map
Figure 1. Mapped extent
Areas shown in blue indicate the maximum mapped extent of this ecological site. Other ecological sites likely occur within the highlighted areas. It is also possible for this ecological site to occur outside of highlighted areas if detailed soil survey has not been completed or recently updated.
Associated sites
R009XY018OR Cold Loamy 17-24 PZ
Mountain Loamy 17-24" PZ
R009XY022OR Cold Shallow 13+ PZ
Mountian Shallow 13"+ PZ
R009XY027OR Cold Very Shallow 13+ PZ
Mountain Very Shallow 13" + PZ
Similar sites
R009XY034OR Cold South 13-17 PZ
Mountian South 13-17" PZ (lower Production)
R009XY036OR Cold Shallow South 13+ PZ
Mountain Shallow South 13"+ PZ
Table 1. Dominant plant species
Tree Not specified
Shrub Not specified
Herbaceous Not specified
Physiographic features
This site occurs near and within forestland on the backslopes of canyons, tablelands, and mountain plateaus north of the Wallowa Mountains. It is typicaly on slopes with south and southwest aspects as one of the last grassland sites before and within the forest. Slopes range from 12 to 60%. Elevation varies from 4000 to 5000 feet.
Table 2. Representative physiographic features
Landforms (1) Mountain
(2) Plateau
(3) Canyon
Elevation 1219 – 1524 m Slope 12 – 60 % Aspect S, SW Climatic features
The annual precipitaton ranges from 17 to 24 inches most of which occurs in the form of snow during the months of November through March followed by ample spring rainfall. Localized, occasionally severe, convectional storms occur during the summer. The soil temperature regime is frigid with a mean annual air temperature of 44 degrees F. Teh frost-free period ranges from 70 to 95 days. The optimum period for plant growth is from late March to late June.
Table 3 Representative climatic features
Frost-free period (average) 100 days Freeze-free period (average) Precipitation total (average) 610 mm ">Influencing water features
Soil features
The soils of this site are moderately deep over basalt bedrock and are well drained. Areas of rock outcrop and talus are common. Typically the surface layer is a very cobbly silt loam to a very stony clay loam. The subsoil varies from a very cobbly clay loam to an extremely cobbly clay. Depth to bedrock is typically less than 30 inches. Permeabilty is moderately slow and the available water holding capacity (AWC) is aboyut 3 to 5 inches for the profile. The potential for erosion, particularly on steep slopes, is severe.
Table 4. Representative soil features
Surface texture (1) Very cobbly silt loam
(2) Very stony clay loam
Family particle size (1) Clayey
Drainage class Well drained Permeability class Moderately slow Ecological dynamics
Range in Characteristics:
Changes in precipitation and elevation have little effect on composition and yeild. Steep due south slopes will ahve the most bluebunch wheatgrass. Idaho fescue will be highest in compostition on moderate southeasterly and westerly slopes. Production is lowest as the soil approaches 20 inches of depth and as coarse fragments increase. Soils close to 40 inches of depth and with few coarse fragments will have the highest propduction.
Response to Disturbance:
If the condition of the site deteriorates as a result of overgrazing, Idaho fescue decreases first followed by bluebunch wheatgrass. Unpalatable forbs increase. Canada and Kentucky bluegrass invade along with soft chess, cheatgrass, salsify and a variety of other unpalatable forbs. Under deteriorated conditions, annuals dominate, bare ground increases and excessive erosion in the bare interspaces reduces the potential of teh site and contributes to downstream sedimentation.State and transition model
Custom diagramStandard diagram
More interactive model formats are also available. View Interactive Models
More interactive model formats are also available. View Interactive Models
Click on state and transition labels to scroll to the respective textEcosystem states
State 1 submodel, plant communities
State 1
Historic Climax Plant CommunityCommunity 1.1
Historic Climax Plant CommunityThe potential native plant community is dominated by bluebunch wheatgrass, Idaho fescue and cinquefoil. Sandberg bluegrass, lupine, arrowleaf balsamroot, yarrow, penstemon and a variety of other forbs are prominent in the stand. Rose and other shrubs are occasionally present. The vegetative composition of the community is approximately 85 percent grasses, 13 percent forbs and 2 percent shrubs.
Figure 2. Annual production by plant type (representative values) or group (midpoint values)
Table 5. Annual production by plant type
Plant type Low
(kg/hectare)Representative value
(kg/hectare)High
(kg/hectare)Grass/Grasslike 1130 1538 1946 Forb 63 149 235 Shrub/Vine 31 47 63 Total 1224 1734 2244 Additional community tables
Table 6. Community 1.1 plant community composition
Group Common name Symbol Scientific name Annual production () Foliar cover (%) Grass/Grasslike1 Perennial Deep-rooted Dominant 1098–1883 bluebunch wheatgrass PSSP6 Pseudoroegneria spicata 785–1255 – Idaho fescue FEID Festuca idahoensis 314–628 – 4 Perennial Shallow-rooted Sub-dominant 31–63 prairie Junegrass KOMA Koeleria macrantha 16–31 – Sandberg bluegrass POSE Poa secunda 16–31 – Forb7 Perennial All Dominant 31–94 lupine LUPIN Lupinus 16–47 – cinquefoil POTEN Potentilla 16–47 – 8 Perennial All Sub-dominant 16–31 common yarrow ACMI2 Achillea millefolium 16–31 – 9 PPFF 16–110 milkvetch ASTRA Astragalus 2–12 – arrowleaf balsamroot BASA3 Balsamorhiza sagittata 2–12 – Indian paintbrush CASTI2 Castilleja 2–12 – buckwheat ERIOG Eriogonum 2–12 – old man's whiskers GETR Geum triflorum 2–12 – Scouler's woollyweed HISC2 Hieracium scouleri 2–12 – western stoneseed LIRU4 Lithospermum ruderale 2–12 – beardtongue PENST Penstemon 2–12 – mule-ears WYAM Wyethia amplexicaulis 2–12 – Shrub/Vine13 Perennial Deciduous Dominant 31–63 rose ROSA5 Rosa 16–31 – common snowberry SYAL Symphoricarpos albus 16–31 – Interpretations
Animal community
Livestock Grazing:
This site is suited to use by cattle and sheep in the late spring and fall. As this site often occurs on both steep and rocky slopes, these limitations need to be carefully considered in developing alternatives. Care should be taken to avoid trampling damage and soil compaction when soils are wet.
Wildlife:
This site is important as a late winter, early spring feeding site for deer and elk. It is often free of snow during the late winter and is one of the first soil areas to warm up. Early green forage is available. Adjacent forested areas provide valueable escape, hiding and thermal cover. As a critical site for deer and elk adverse impacts can easily result without careful management.
Native Wildlife Associated With The Potential Climax Community:
Rodents, Songbirds, Red-tailed hawk, Coyote, Rocky Mountian elk, and Mule deer.Hydrological functions
The hydrologic cover condition is good at higher condidtion classes. The soils are in hydrologic group C.
Recreational uses
North of the Wallowa Mountains this site occurs in complex with other sites near and within forestland. It adds to the view with the distant mountains and high canyon slopes.
Other information
This site has a low potentail for range seeding because of coarse fragments being in complex with shallower sites and/or steepness of slope.
Supporting information
Contributors
A. Bahn
Cici Brooks
Justin GredvigApproval
Kirt Walstad, 5/05/2025
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) Jeff Repp Contact for lead author Oregon State Rangeland Management Specialist Date 07/30/2012 Approved by Approval date Composition (Indicators 10 and 12) based on Annual Production Indicators
-
Number and extent of rills:
None to some, severe sheet & rill erosion hazard -
Presence of water flow patterns:
None to some -
Number and height of erosional pedestals or terracettes:
None to some -
Bare ground from Ecological Site Description or other studies (rock, litter, lichen, moss, plant canopy are not bare ground):
5-10% -
Number of gullies and erosion associated with gullies:
None -
Extent of wind scoured, blowouts and/or depositional areas:
None, slight wind erosion hazard -
Amount of litter movement (describe size and distance expected to travel):
Fine - limited movement -
Soil surface (top few mm) resistance to erosion (stability values are averages - most sites will show a range of values):
Moderately to significantly resistant to erosion; aggregate stability = 3-6 -
Soil surface structure and SOM content (include type of structure and A-horizon color and thickness):
Moderately deep, well drained, with areas of rock outcrop and talus and with a very cobbly silt loam to a very stony clay loam surface; low to moderate OM (1-3%) -
Effect of community phase composition (relative proportion of different functional groups) and spatial distribution on infiltration and runoff:
Significant ground cover (80-90%) and steep slopes (12-60%) moderately to significantly limit rainfall impact and overland flow -
Presence and thickness of compaction layer (usually none; describe soil profile features which may be mistaken for compaction on this site):
None -
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:
Bluebunch wheatgrass > Idaho fescue > dominant forbs > other forbs > other grasses = shrubsSub-dominant:
Other:
Additional:
-
Amount of plant mortality and decadence (include which functional groups are expected to show mortality or decadence):
Normal decadence and mortality expected -
Average percent litter cover (%) and depth ( in):
-
Expected annual annual-production (this is TOTAL above-ground annual-production, not just forage annual-production):
Favorable: 1800, Normal: 1400, Unfavorable: 1000 lbs/acre/year at high RSI (HCPC) -
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:
With deterioration of plant community, bluegrasses, annual bromes, and medusahead invade sites that have lost deep rooted perennial grass functional groups. Excessive erosion may occur, deteriorating site potential. -
Perennial plant reproductive capability:
All species should be capable of reproducing annually
Print Options
Sections
Font
AAAAOther
PrintThe Ecosystem Dynamics Interpretive Tool is an information system framework developed by the USDA-ARS Jornada Experimental Range, USDA Natural Resources Conservation Service, and New Mexico State University.
Accessibility statement